the Creative Commons Attribution 4.0 License.
the Creative Commons Attribution 4.0 License.
Liquid Polymer Enhances Methanogenesis and Restructures Prokaryotic Communities in Freshwater Sediments
Abstract. The widespread use of synthetic hydrophilic polymers, such as polyvinylpyrrolidone (PVP), has raised concerns about their potential effects on environmental biogeochemical processes, yet their impact on sediment ecosystems remains largely unexplored. We investigated how PVP influences methane (CH4) production and prokaryotic community composition in freshwater sediments over a 56-day anoxic incubation. PVP exposure accelerated the onset of methanogenesis, increased maximum CH4 production rates, and elevated maximum CH4 concentrations. These functional changes were accompanied by shifts in bacterial communities, particularly an enrichment of fermentative Clostridia, which generate key substrates for methanogens (H₂, acetate, and formate). Nonetheless, archaeal communities, including methanogens, exhibited comparatively minor or transient responses. Mechanistically, enhanced CH4 production likely resulted from a combination of increased substrate availability, altered redox microenvironments, and indirect reductions in competing electron acceptors. Our results suggest that PVP modifies sediment carbon cycling through complex microbial, biogeochemical, and physical interactions rather than direct toxicity to methanogens. These findings highlight the need to consider both chemical and physical effects of synthetic hydrophilic polymers on sediment microbial ecosystems and greenhouse gas emissions, and they underscore the importance of targeted studies to quantify these impacts in natural environments.
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RC1: 'Comment on egusphere-2026-1216', Anonymous Referee #1, 14 Apr 2026
- AC1: 'Reply on RC1', Alexander Feckler, 17 Aug 2026
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RC2: 'Comment on egusphere-2026-1216', Anonymous Referee #2, 22 Jul 2026
The manuscript evaluates the methane production potential during a 56-day anoxic incubation of sediments after amendment of polyvinylpyrrolidone (PVP). PVP was used as a representative of synthetic hydrophilic polymers (SHP), which are increasingly used and released into the environment. Results indicated the presence of PVP increase the CH4 production potential and influences the microbial community.
I am less qualified to evaluate technical molecular biology details and the microbial community aspects, so this review focuses on the other parts of the manuscript.
I find the focus on SHP interesting, and in general found this study well-executed and the manuscript well-written. However, I have some questions that require clarifications.
How much SHP/PVP can be expected to reach sediments? Why are sediments a key environment to evaluated effects of SHP/PVP in?
L55. How can PVP be chemically stable if it has clear effects on sediment carbon cycling in the experiment?
Please express sediment carbon content including the leaf powder addition and PVP with comparable units so it is possible to relate all components with the sediment carbon budget and the CH4 formation.
L77-78: Why are wastewater treatment plants increasing the PVP concentrations 8-70-fold compared to sewage water?
L81. pH adjustment: Please tell more about this pH sensitivity. How sensitive would PVP degradation or other experimental results be to pH? What are the implications of this for the results? How valid are the results in situ t other pH levels?
L95-97 and Table1: It seems the two lowest levels of PVP amendment (0,5 and 50 mg/L) are below LOQ (70 mg/L), and initial measurements at 50 and 5000 mg/L were <80% of the amendments. Please explain why there is such a large discrepancy. How robust is the method? What was the background PVP level in the original sediment?
Eq 1. The final addition of xe is unclear. What does this mean? Why is it needed? Perhaps I misunderstand, but in later equations the number of moles in the headspace and the water is calculated separately and summed to derive the total amount, and that should take care of all partitioning between headspace and water, and a mole fraction correction as expressed in Eq1 seems strange?
Results and Fig. 1: So, over a PVP-addition range from 0 to 5000, the CH4 production potential increase 20% (1.2-fold). 30% (approx.) of this increase occur happen when the PVP addition increased from 0 to 0.5. The rest happens when increasing PVP 50 000-fold. Accordingly, although the results are significant, the response on CH4 is rather modest in relation to the very large change in PVP concentrations. Please discuss this and what it could mean in the manuscript. Is it possible that this effect is linked to something else than PVP given the experimental setup, or can that be excluded? Are that any alternative interpretations of the results?
Citation: https://doi.org/10.5194/egusphere-2026-1216-RC2 - AC2: 'Reply on RC2', Alexander Feckler, 17 Aug 2026
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I very much appreciate the motivation behind this paper and think that the introduction reads quite nicely. However, the paper only contains 2 main text figures, which I do think is insufficiently short to tell a compelling mechanistic story as the authors are intending to do per the discussion. While I certainly see value in this experiment, I do not think the paper shows enough as written – to me, it reads as an introduction to a list of hypotheses instead of actually a demonstration mechanism, and the discussion/conclusion emphasizes those hypotheses over analysis of the data in hand. I think follow up experimentation/laboratory analyses on these reactors could be extremely beneficial to help support the ideas that are put forth in the discussion, to strengthen the merits of the study on its own accord. The bones of a good experimental paper are here, but as it currently stands, I do not think there is sufficient data or analysis to warrant publication currently.
Specific comments:
Introduction: I think this section reads very well!
Methods:
Results:
Discussion