The research team, led by Zuzanna Prus-Frączek and including senior authors Katarzyna Styszko and Małgorzata Wilk, focused on polyethylene terephthalate, or PET, the polymer of water bottles and food packaging, and polystyrene, or PS, the aromatic plastic found in insulation, packaging foam, and countless disposable items. Both are among the most common polymers recovered from treated sludge, which can harbor hundreds to thousands of microplastic particles per kilogram of dry matter. Because European Union policy increasingly promotes the reuse of sludge as fertilizer and soil amendment on farmland, understanding whether hydrothermal treatment truly breaks these particles down is not an academic detail. It is central to whether plastic pollution quietly rides the circular economy back into the food chain.

Earlier studies had reported that hydrothermal carbonization can slash the number of microplastic particles detectable in sludge by up to 90 percent, with one study showing removal of particles larger than 50 micrometers jumping from about 11 percent to 85 percent as temperatures rose from 170 to 220 degrees Celsius. But a reduction in detectable particles is not the same as destruction. Fragments can shatter below the size limits of analytical instruments, and polymer-derived compounds can dissolve into the surrounding water without ever being mineralized. The Polish team set out to determine which of these fates actually befalls PET and PS, treating the two polymers separately in pure water at 220 degrees Celsius for one, two, and three hours, conditions carefully chosen to mirror real sewage sludge processing while eliminating interference from sludge-derived organic matter.

The results revealed a striking asymmetry between the two plastics. PET, whose backbone contains ester bonds that water can chemically attack, proved far more vulnerable. Thermogravimetric analysis showed that its degradation onset temperature, which stands at roughly 402 degrees Celsius in the raw polymer, plummeted to between 246 and 284 degrees Celsius after treatment. The pyrolytic residue left at 800 degrees Celsius collapsed from 12.7 percent to as little as 1.3 percent, indicating a severely diminished tendency to form stable carbon structures. Infrared and Raman spectroscopy painted a consistent picture: the sharp ester carbonyl band at 1714 inverse centimeters gave way to new dominant components near 1671 to 1677 inverse centimeters, signaling a heterogeneous mix of partially hydrolyzed ester bonds and newly formed oxygen-containing structures. Scanning electron microscopy showed surfaces transformed from smooth and compact into rough, cracked, and cavity-riddled landscapes.

Polystyrene, by contrast, emerged from the reactor remarkably intact. Its hydrophobic aromatic skeleton, held together by carbon-carbon bonds that water cannot easily cleave, resisted the conditions that visibly weakened PET. Treated PS samples retained a single-step thermal degradation profile with maximum decomposition temperatures of around 416 to 417 degrees Celsius, essentially unchanged from the raw material. The principal FTIR and Raman bands, including the characteristic aromatic ring breathing mode near 1001 inverse centimeters, remained within measurement uncertainty of their original positions. Only slight band broadening after three hours hinted at limited local disorder at the surface. The finding aligns with earlier work showing that complete PS decomposition demands 360 degrees Celsius and four hours, conditions far more severe than any sewage sludge reactor would employ.

Perhaps the most consequential discovery came from analyzing the process water itself. When the researchers measured chemical oxygen demand and total organic carbon in the liquid phase, PET proved to be a prodigious polluter. Normalized to the initial polymer mass, PET released approximately 737 to 876 milligrams of COD and 320 to 343 milligrams of TOC per gram of plastic into the water, with absolute concentrations reaching 6145 to 7300 milligrams per liter of COD and around 2700 to 2855 milligrams per liter of TOC. Polystyrene, in comparison, contributed only 35 to 83 milligrams of COD and 99 to 140 milligrams of TOC per gram of polymer. The pH of the PET process water remained stubbornly acidic, between 3.8 and 3.9, consistent with the accumulation of acidic products from ester bond cleavage, while phenolic compounds slowly increased with longer treatment, suggesting the formation of refractory aromatic derivatives that resist further degradation.

These numbers carry a direct message for engineers designing full-scale sludge hydrothermal carbonization plants. Process water from sludge HTC is already heavily loaded with dissolved organics and can contain inhibitory or toxic compounds, and adding a substantial polymer-derived burden, particularly from PET-rich sludge, would amplify the challenge of treating or safely recirculating that water. Previous pilot-scale studies have shown that biological treatment of HTC process water can achieve COD removals of roughly 71 to 75 percent in membrane bioreactors and sequencing batch reactors, but the researchers caution that the added plastic-derived load could strain these systems further. Hydrochar yields added another layer of nuance: the most intensive apparent conversion for both polymers occurred at two hours, with yields for PS dropping to 75.6 percent and PET to 53.6 percent, and the non-monotonic trends hint at competing processes of depolymerization, dissolution, and secondary condensation of soluble intermediates back onto the solid phase.

The environmental implications extend beyond the treatment plant. Hydrochar from PET-containing sludge, with its weakened structure and earlier degradation onset, would likely be more susceptible to further fragmentation, oxidation, and weathering if applied to soils, potentially generating new generations of smaller plastic particles. The dramatic reduction in pyrolytic residue also suggests a diminished capacity for stable carbon sequestration in PET-derived char, undermining one of the climate arguments for hydrochar use in agriculture. Polystyrene-derived material, meanwhile, may remain embedded within or incorporated into the carbonized matrix despite surface alteration, retaining its aromatic identity. In neither case does the plastic vanish. As the authors put it, HTC should be understood primarily as a polymer-transformation and redistribution process, shifting material between the solid, liquid, and gas phases rather than eliminating it from the system.

The study does have limits that the team acknowledges candidly. The experiments used pristine, manually fragmented waste plastics in distilled water at a single temperature, rather than environmentally aged particles in a real sludge matrix, and the analyses could not identify specific molecular transformation products, distinguish hydrolysis from oxidation, or assess nanoplastic formation because samples were ground before imaging. Future work, the researchers argue, should incorporate real sewage sludge, replicate experiments across broader operating windows, and deploy gas and liquid chromatography coupled with mass spectrometry to identify individual compounds, alongside leaching and ecotoxicity tests to evaluate the fate of released organics in soils. For now, the message for the water sector is clear and somewhat uncomfortable: hydrothermal carbonization remains a valuable technology for valorizing wet sludge, but claims of microplastic removal must be read as claims of microplastic transformation, and any credible plant design must treat the process water as a first-class waste stream, not an afterthought.

Subject of Research: Hydrothermal carbonization of PET and polystyrene microplastics under sewage sludge treatment conditions

Article Title: Hydrothermal carbonization of PET and PS microplastics under conditions relevant to sewage sludge treatment

Article References: Prus-Frączek, Z., Kalemba-Rec, I., Magdziarz, A., Dróżdż, A., Chwiej, J., Styszko, K., & Wilk, M. (2026). Hydrothermal carbonization of PET and PS microplastics under conditions relevant to sewage sludge treatment. Energy Reports, 16, Article 109697. https://doi.org/10.1016/j.egyr.2026.109697

Image Credits: AI Generated

DOI: 10.1016/j.egyr.2026.109697

Keywords: microplastics, hydrothermal carbonization, sewage sludge, PET, polystyrene, hydrochar, process water, wastewater treatment, COD, TOC, polymer degradation, circular economy

Microplastics, defined as solid polymeric particles smaller than 5 millimeters, have become an emerging concern worldwide. They arise either from deliberately manufactured microscopic materials, so-called primary microplastics, or from the progressive fragmentation of larger plastic objects exposed to physical, chemical, and biological weathering, known as secondary microplastics. Wastewater treatment plants sit squarely on the front lines of this pollution pathway. They receive enormous loads of plastic fibers and fragments from household laundry, cosmetic products, and urban runoff, yet they also act as concentrators, retaining a significant fraction of the incoming plastic in the sludge line. When that sludge is reused on land or improperly disposed of, it can become a secondary source of contamination for soils and waterways. Understanding exactly how many particles flow through these facilities—and what they are made of—depends on analytical methods that can reliably pry plastic particles out of a sea of organic matter without destroying the evidence in the process. That is precisely the challenge the new research set out to solve.

Led by Ivanilson da Silva de Aquino of the University of Brasília, together with colleagues at the UnB Planaltina Faculty and the Federal University of Jequitinhonha and Mucuri Valleys, the team built its methodological framework from the ground up. The first step was to manufacture reference microplastics from the six commodity polymers that dominate urban plastic waste streams: polyethylene terephthalate, high-density polyethylene, low-density polyethylene, polyvinyl chloride, polypropylene, and polystyrene. These laboratory-made particles, produced as irregular fragments ranging from 0.1 to 3.0 millimeters, served as benchmarks against which every subsequent processing step could be tested. Before any chemistry was attempted, the researchers confirmed by attenuated total reflectance Fourier-transform infrared spectroscopy—ATR-FTIR for short—that each batch of reference particles displayed the characteristic absorption patterns of its parent polymer, ensuring that the starting materials were spectroscopically unambiguous.

The heart of the new protocol is a digestion step based on Fenton’s reagent, a mixture of hydrogen peroxide and iron catalyst that generates highly reactive hydroxyl radicals capable of shredding organic matter. Wastewater and sludge samples are so loaded with organic material, microbial biomass, and inorganic debris that microscopic plastic particles would otherwise be invisible. The catch is that the digestion must be aggressive enough to clear the matrix but gentle enough to leave the plastics themselves chemically intact. If the polymers are oxidized too severely, their infrared fingerprints can shift, complicating identification, and in some cases particles can fragment or lose mass entirely. The team therefore subjected its six reference polymers to five different Fenton protocols spanning temperatures from 30 to 80 degrees Celsius and various reaction durations, then scrutinized the consequences using FTIR and a metric known as the carbonyl index.

The carbonyl index tracks the relative abundance of carbon-oxygen double bonds on polymer surfaces, a hallmark of oxidative degradation. Because polyolefins such as polyethylene and polypropylene naturally lack carbonyl groups, even small increases in the index reveal genuine surface oxidation. The results were revealing. At 30 degrees Celsius the reaction was too sluggish to digest organic matter effectively. Above 80 degrees Celsius oxidation became severe, with polyethylene terephthalate and polypropylene showing the largest changes in carbonyl absorption. But in the moderate window between 40 and 60 degrees Celsius, with a reaction time of about two hours, the Fenton treatment delivered the best of both worlds: organic matter was substantially degraded, while the carbonyl index of all tested polymers showed no significant changes. FTIR spectra recorded before and after digestion showed no meaningful spectral deviations, meaning the polymeric fingerprints needed for reliable identification survived the chemical assault intact.

With digestion optimized, the researchers turned to the second major hurdle: separating buoyant plastic particles from the remaining debris. Density separation exploits the simple physical fact that most common polymers are less dense than suitable salt solutions, so they float while heavier mineral and organic particles sink. The team built a custom separation device and systematically compared separation media. Plain water, with a density of 1.0 grams per cubic centimeter, performed poorly because more than half of the target polymers are denser than water and simply sank. Saturated sodium chloride solution, the cheap and inert classic, reached about 1.2 grams per cubic centimeter and successfully floated roughly two-thirds of the studied plastics—but it excluded the high-density polymers polyvinyl chloride, at 1.10 to 1.45 grams per cubic centimeter, and polyethylene terephthalate, at 1.37 to 1.45 grams per cubic centimeter. Relying on sodium chloride alone, the authors caution, could systematically underestimate microplastic abundance.

Zinc chloride proved to be the decisive upgrade. At concentrations reaching 1.6 and 1.8 grams per cubic centimeter, zinc chloride solutions kept every polymer tested in suspension, allowing effective recovery of even the heaviest particles. In the validation experiments, the densest solution ensured that all target polymers remained in the floating fraction, minimizing losses during sample processing. The researchers note, however, that the analytical superiority of zinc chloride comes with trade-offs: its toxicity, higher operational cost, and disposal requirements must be weighed when designing routine monitoring programs, and reuse of the solution can help mitigate cost and waste.

The true test came when the optimized protocol was unleashed on real samples from a full-scale facility, the Brasília North wastewater treatment plant. The researchers deliberately chose two matrices representing opposite ends of the processing complexity spectrum: raw wastewater, with a chemical oxygen demand averaging 882.7 milligrams of oxygen per liter, and dewatered sewage sludge, whose chemical oxygen demand averaged a staggering 30,600 milligrams of oxygen per liter—roughly thirty-five times higher. Applying the optimized Fenton protocol cut chemical oxygen demand by 81.3 percent in the raw wastewater and 82.3 percent in the sludge, leaving values of 165.4 and 5,420 milligrams of oxygen per liter respectively. Visually, the transformation was dramatic: dark, turbid samples became noticeably clearer and more translucent after treatment, although sludge samples, given their enormous organic load, sometimes required a second digestion cycle to remove residual suspended material.

Following digestion, density separation with zinc chloride at 1.8 grams per cubic centimeter produced striking stratification in the custom unit, with a floating fraction enriched in microplastics accumulating at the top and residual organic matter and denser inorganic particles settling at the bottom. Spiked reference particles of every polymer type were successfully recovered from both matrices, including the notoriously difficult polyethylene terephthalate and polyvinyl chloride. The researchers then applied the validated workflow to hunt for native microplastics—particles that arrived in the samples from the real world rather than from the laboratory. Stereomicroscopy revealed a rich menagerie of fragments, films, and fibers varying widely in color, size, and surface texture, exactly the heterogeneity expected from the diverse plastic sources entering urban sewer networks.

ATR-FTIR analysis of the recovered native particles confirmed the method’s analytical power. Polyethylene emerged as the dominant polymer in both wastewater and sludge, identified through its characteristic absorption bands near 2915, 2845, 1462, and 717 wavenumbers, corresponding to carbon-hydrogen stretching, methylene bending, and rocking vibrations. A subtle band near 1377 wavenumbers even allowed the team to distinguish low-density from high-density polyethylene. Crucially, the spectra of environmental particles retained all the features needed for identification, confirming that the upstream pretreatment had not compromised the spectroscopic evidence. The predominance of polyethylene aligns with the ubiquity of packaging films and containers in urban life and echoes findings from previous studies around the world.

The significance of this work extends well beyond a single treatment plant in the Brazilian capital. By demonstrating that Fenton digestion, zinc chloride density separation, stereomicroscopy, and ATR-FTIR can operate as a coherent, validated pipeline across both liquid and solid waste streams, the study provides exactly the kind of methodological scaffolding that the field has lacked. The authors emphasize that their framework can support future monitoring programs aimed at evaluating the occurrence, transport, and fate of microplastics throughout wastewater treatment systems, and that it contributes to the ongoing effort to establish standardized protocols for microplastic analysis in complex environmental matrices. As regulators and researchers worldwide push to quantify how much plastic flows from drains to rivers to oceans—and how much lingers in the sludge spread across farmland—reliable, reproducible measurements will be the foundation of every policy decision. This new protocol offers a tested blueprint for generating them.

Microplastics, defined as plastic particles less than five millimeters in diameter, are now ubiquitous across marine, freshwater, and even terrestrial environments. Their persistence and widespread distribution pose multifaceted problems, affecting biodiversity, ecosystem functions, and ultimately human health through bioaccumulation in food webs. The original framework proposed by Mehinto et al. offered a structured approach to risk assessment and management, emphasizing the interconnectedness of ecological, chemical, and socio-economic factors. This latest correction underscores refinements in risk parameters, methodologies, and potential mitigation strategies, reflecting how nuanced and evolving our understanding of microplastic impacts continues to be.

One of the pivotal challenges in assessing microplastic risk lies in the particles’ diverse physicochemical properties. Variations in size, shape, polymer type, and chemical additives significantly influence their environmental fate and toxicity. The correction to this framework addresses these complexities by incorporating refined metrics that better capture the heterogeneity of microplastic particles in different aquatic environments. This advancement allows scientists and policymakers to calibrate risk assessments more precisely, enhancing the accuracy of predictions regarding ecological and human health outcomes.

The aquatic ecosystems are especially vulnerable due to microplastics’ ability to adsorb and concentrate hazardous chemicals, including persistent organic pollutants and heavy metals. This sorption capability transforms microplastics into vectors of chemical pollution, transporting toxic substances across ecosystems and biogeochemical cycles. The updated risk management framework integrates this dimension, advocating for the consideration of pollutant-loaded microplastics in future environmental monitoring and remediation efforts. This multidimensional approach deepens our understanding of microplastic pollution as a complex stressor in aquatic environments.

Crucial to effective management is the implementation of adaptive regulatory measures. The correction emphasizes a dynamic model where risk thresholds and protective actions are periodically revised based on emerging scientific evidence. Such an approach is critical given the rapid scientific advances and growing datasets on microplastic distribution and effects. By promoting regulatory flexibility, this framework supports responsive governance structures capable of mitigating risks before they escalate into irreversible environmental damage.

Furthermore, the framework correction elucidates the importance of integrating ecological risk assessments with socioeconomic factors. Microplastics have implications beyond environmental health, affecting fisheries, tourism, and community livelihoods dependent on aquatic resources. The corrected model proposes more robust socioeconomic impact analyses alongside ecological assessments, fostering holistic management strategies. This integration highlights the necessity of interdisciplinary collaboration across ecology, toxicology, economics, and social sciences to devise sustainable solutions.

From a technological standpoint, the refined framework suggests enhanced methodologies for detecting and quantifying microplastics in water bodies. Advances in spectroscopic and microscopic techniques, coupled with machine learning algorithms, enable more sensitive, rapid, and cost-effective analyses. These technological improvements are vital for monitoring programs, enabling the generation of comprehensive datasets necessary to inform adaptive management. The correction reflects these technological trends by recommending standardization of detection protocols to ensure data comparability and reliability.

Another notable aspect addressed by the correction involves the ecological risk pathways specific to different aquatic habitats, such as rivers, estuaries, and oceans. Each habitat type experiences unique hydrodynamic conditions and biological communities, influencing microplastic transport, deposition, and impact patterns. By tailoring risk management frameworks to habitat-specific contexts, the updated model fosters targeted interventions that optimize resource allocation and ecological protection outcomes across diverse aquatic systems.

The amendment also places significant emphasis on downstream impacts, including microplastic accumulation in sediments and interactions with benthic organisms. This sediment-phase focus reveals a critical yet often underappreciated reservoir for microplastic pollutants, where prolonged exposure can induce chronic effects on sediment-dwelling species. Recognizing sediment as both a sink and potential source for secondary microplastic pollution expands the scope of environmental monitoring and highlights the need for integrated sediment management in pollution control strategies.

Public awareness and community engagement remain central pillars for effective microplastic risk management, as articulated in the correction. The framework encourages transparent communication channels between scientists, policymakers, and stakeholders, including local communities and industries. Elevating public understanding of microplastic sources, pathways, and consequences can facilitate behavioral changes, support grassroots initiatives, and drive policy acceptance. This participatory approach underscores the social dimensions of environmental governance in addressing global pollution challenges.

Importantly, this correction underscores the value of international cooperation in tackling microplastic pollution. Given the transboundary nature of aquatic ecosystems and plastic debris movement, coordinated efforts across countries and regions are imperative. The framework advocates for harmonized monitoring protocols, data sharing platforms, and joint policy actions to strengthen collective capacity in microplastic risk mitigation. This global perspective resonates with broader environmental treaties and sustainability agendas prioritizing biodiversity conservation and pollution reduction.

The authors also reaffirm the critical need for future research directions to fill persisting knowledge gaps. These include long-term ecotoxicological studies on microplastic effects across trophic levels, the role of microplastics in disease transmission, and potential synergistic impacts with climate change stressors. Addressing these uncertainties will further refine risk model parameters and support evidence-based policymaking. The correction invites the scientific community to collaborate in multidisciplinary efforts that enhance predictive capabilities and management effectiveness.

A particularly forward-looking element involves integrating emerging technologies such as remote sensing and environmental DNA (eDNA) analyses to detect and monitor microplastic pollution. These innovations promise to revolutionize environmental surveillance by enabling large-scale, non-invasive assessments of microplastic distribution and ecological impacts. The revised framework recognizes these technologies’ potential, advocating their incorporation into future monitoring networks to provide real-time data with unprecedented spatial coverage and resolution.

Furthermore, the correction sheds light on potential remediation technologies aimed at reducing microplastic loads in aquatic ecosystems. Approaches such as biofiltration, advanced wastewater treatment, and plastic-eating enzymes are discussed as promising yet still experimental strategies. The framework stresses the importance of rigorous evaluation of these interventions’ ecological footprint and effectiveness before widespread adoption. Balancing innovation with environmental safety remains a key consideration in microplastic pollution management.

In conclusion, the correction to the risk-based management framework for microplastics in aquatic ecosystems represents a pivotal advancement in addressing one of the most pervasive environmental pollutants of our time. By incorporating refined risk parameters, adaptive governance models, technological innovations, and socio-economic integrations, this updated framework offers a comprehensive blueprint for science-driven, effective management. As microplastic pollution continues to challenge ecosystem resilience and human well-being, such evolving frameworks are crucial for steering global efforts toward sustainable aquatic health futures.

Subject of Research: Risk-based management of microplastics in aquatic ecosystems

Article Title: Correction to: Risk-based management framework for microplastics in aquatic ecosystems

Article References:
Mehinto, A.C., Coffin, S., Koelmans, A.A. et al. Correction to: Risk-based management framework for microplastics in aquatic ecosystems. Microplastics & Nanoplastics 5, 41 (2025). https://doi.org/10.1186/s43591-025-00149-2

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