Chlorine Dioxide and Reverse-Osmosis Membrane Compatibility

    An evidence-led guide for understanding biofilm in managed water and hygiene systems.

    Evidence-led guidance
    Expert Reviewed

    Chlorine dioxide is used upstream of reverse-osmosis systems for biofouling control, but 2026 laboratory studies show that polyamide membranes are not immune to it: concentration, pH and exposure time all govern whether the selective layer is damaged.

    The 2026 RSC Advances study

    A study first published in RSC Advances on 21 July 2026 (Arliyani et al., Institut Teknologi Sepuluh Nopember, doi 10.1039/d5ra09010e) exposed thin-film composite polyamide reverse-osmosis membrane coupons to chlorine dioxide at different concentrations and pH values, then assessed them by permeate flux, scanning electron microscopy with elemental analysis, and contact-angle measurement.

    Higher chlorine dioxide concentration and alkaline pH accelerated degradation: permeate flux rose (a sign of a compromised selective layer), surfaces deformed and cracked, elemental composition shifted and wettability changed. The mildest condition tested, 0.5 ppm chlorine dioxide at pH 6, produced the least structural change and stayed closest to the untreated membrane. The authors describe this as the most favourable balance between preserving the membrane and retaining the disinfectant's operational advantages. Importantly, they note that biofouling itself was not measured; no microbial adhesion or biofilm-growth experiments were run.

    Related 2026 membrane evidence

    A separate study in the Journal of Environmental Chemical Engineering (Wang et al., April 2026, doi 10.1016/j.jece.2026.122119) treated a fully aromatic polyamide membrane (NF90) with chlorine dioxide for 96 hours at neutral pH. It reported increased pore size and surface roughness, greater hydrophilicity and water permeability up to 63% higher, with solute passage rising more steeply. Unlike chlorination, no halogen incorporation into the polymer was detected even at 250 mg/L as Cl₂; the proposed mechanism was hydrolytic breakage of amide bonds. The authors characterise polyamide degradation by chlorine dioxide as slower than by chlorine, but real.

    Read together, the two studies agree on direction: chlorine dioxide attacks polyamide more slowly than free chlorine and by a different route, but it does attack it, and the rate rises with concentration, exposure time and (in the RSC study) pH. Statements that chlorine dioxide 'does not react' with polyamide are not supported by this evidence.

    What these studies do and do not establish

    They establish that polyamide membrane damage from chlorine dioxide is a function of dose, pH and time, and that low concentrations near neutral-to-slightly-acidic pH caused the least change in laboratory exposure. They give operators a reason to treat membrane compatibility as a parameter to be specified and monitored, not assumed.

    They do not establish a safe operating envelope for any real plant. Both were bench studies on coupons with the oxidant in continuous contact; neither ran a pressurised element, a full pre-treatment train, or a biofouling challenge, and neither reported long-term rejection data under operating conditions. Membrane manufacturers' warranty limits remain the governing constraint. ChloroKlean products were not tested, and this guide makes no claim about their compatibility with any membrane; confirm with the membrane supplier and the product's technical documentation before any upstream dosing.

    Evidence and uncertainty

    Published biofilm studies are valuable for understanding mechanisms, but their conditions may not match a particular installation. Species, surfaces, deposits and operating conditions should be recorded when interpreting evidence.

    For safety-critical systems, decisions should be documented through the relevant risk assessment and management plan.

    Choosing the next question

    A useful next step is to identify what is known, what is inferred and what needs verification. This avoids treating a general reference as a site diagnosis.

    Where a product is considered, confirm the intended use, authorisation and label directions independently of this educational guide.

    A proportionate biofilm-management approach

    Use this sequence to frame investigation and control; it is not a dosing protocol.

    1

    Define the system and risk

    Map wetted surfaces, operating conditions, users and relevant legal or sector guidance.

    2

    Gather evidence

    Review inspection, operational, residual and microbiological records rather than relying on one indicator.

    3

    Address contributing conditions

    Consider cleaning, hydraulics, nutrients, stagnation and equipment condition alongside any authorised biocide programme.

    4

    Verify and review

    Document the intervention and review results through the site’s written scheme or hygiene plan.

    Expert Insights

    "Biofilm control is a system-management question: chemistry, surfaces, flow, cleaning and verification all matter."

    ChloroKlean Technical Team

    Technical review team

    About the Reviewer

    Gavin Owen

    Managing Director, ChloroKlean

    Gavin Owen leads ChloroKlean's technical and commercial operations, bringing over 20 years of experience in industrial chemical distribution and water treatment. He oversees product development, regulatory compliance strategy, and the company's BPR compliance programme across PT2, PT4, PT5, and PT11 product types. Gavin works directly with water treatment professionals, facilities managers, and public health engineers across healthcare, leisure, food processing, and industrial sectors.

    BPR Compliance
    Water Treatment
    Legionella Control
    Industrial Disinfection

    Frequently Asked Questions

    Common questions about this topic, answered by our technical team.

    Not unconditionally. 2026 laboratory studies show polyamide degrades more slowly under chlorine dioxide than under chlorine, but it does degrade, and the rate increases with concentration, exposure time and alkaline pH. Membrane manufacturer limits should govern any upstream dosing.

    No. The authors state that biofouling was not directly evaluated; they inferred fouling propensity from surface changes. The study is about membrane integrity under oxidant exposure.

    No. Both studies used laboratory chlorine dioxide solutions on membrane coupons. Nothing here is a compatibility claim for any ChloroKlean product.

    Start with the system’s risk assessment, operational records and applicable sector guidance. Use the referenced sources to frame questions, not to replace competent site assessment.

    Scope and safe-use note

    • This is general educational information, not a dosing instruction or a product label.
    • Use only a biocidal product authorised for its intended product type and follow its label, Safety Data Sheet and site risk assessment.
    • Investigate system design, cleaning, monitoring and microbiological findings with a competent person where there is a health risk.

    Published evidence about a disinfectant or another product does not establish efficacy, authorisation or an appropriate use pattern for any ChloroKlean product.

    Related Resources

    Continue exploring our knowledge base and product information.

    Sources & References

    This article references guidance from the following authoritative sources:

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