Chlorine Dioxide vs Ozone for Cooling Towers and Drinking Water

    Chlorine dioxide and ozone are oxidising biocides used in cooling and drinking-water treatment. Ozone acts at the point of dosing, has a short water half-life and can form bromate where bromide is present. Chlorine dioxide can provide a measurable residual and act on biofilm; it forms no chloramines and generally very little THM or HAA, while chlorite and chlorate require control. Selection depends on the system, product conditions and validation. ChloroKlean Plus L20 is supplied in Great Britain under GB BPR transitional arrangements for the applicable in-situ precursor route and its stated PT5 and PT11 uses. No EU or Northern Ireland authorisation is claimed.

    Author
    Key Advantage of ClO₂
    Provides a sustained, measurable residual across the whole distribution system; ozone does not.
    By-products
    ClO₂ forms no chloramines and generally very little THM or HAA; chlorite and chlorate require control. Ozone can form bromate where bromide is present, plus aldehydes and ketones.
    pH Range
    ClO₂ effective at pH 4-10. Ozone effective but consumed faster at higher pH and elevated temperatures.
    Regulatory Sources
    WHO Guidelines for Drinking-water Quality, HSE HSG274 Part 1, US EPA Stage 1 D/DBPR, DWI guidance, EU BPR 528/2012
    UK Compliance
    In Great Britain, check each product, product type and active-substance precursor route. A product may be authorised or lawfully supplied under applicable GB Review Programme transitional arrangements. ChloroKlean Plus L20 is supplied under those transitional arrangements for its stated PT5 and PT11 uses. Article 95 supply-chain status is not product authorisation; no EU or Northern Ireland authorisation is claimed.
    Comparison Guide

    Chlorine Dioxide vs Ozone

    Comparing chlorine dioxide (ClO₂) and ozone (O₃) for cooling towers, drinking water, and industrial water treatment. Residual disinfection, capital cost, and bromate formation all matter.

    ClO₂

    Chlorine Dioxide

    • Sustained residual across distribution system
    • Penetrates biofilm in fill packs and pipework
    • No bromate formation in bromide-containing water
    • No on-site generator required - lower capital cost
    • Effective across pH 4-10
    O₃

    Ozone (O₃)

    • Highest oxidation potential of common biocides
    • Fast point-of-dose efficacy
    • No residual - secondary disinfection still required
    • Forms bromate when bromide is present in source water
    • High capital cost (on-site generator required)

    Detailed Comparison

    Detailed comparison of chlorine dioxide versus ozone
    FeatureChlorine DioxideOzone
    Residual Disinfection

    Yes

    Measurable residual across distribution

    No

    Half-life ~20 minutes in water

    Biofilm Penetration

    Excellent

    Penetrates EPS matrix

    Surface only

    Reacts too fast to diffuse into biofilm

    Bromate Formation

    None

    Does not oxidise bromide to bromate

    Yes

    Regulated DBP in bromide-containing water

    THM / HAA Formation

    Generally very little

    Control chlorite, chlorate and other by-products

    Generally little

    Control bromate and other oxidation products

    Capital Cost

    Low

    Liquid biocide, simple dosing pump

    High

    On-site generator and contactor required

    Energy Use

    Low

    No on-site generation

    High

    Continuous electrical generation

    Legionella Efficacy

    Proven

    >4-log reduction documented

    Proven at point of dose

    But no downstream residual protection

    pH Range Effectiveness

    pH 4-10

    Performance largely independent of pH

    Reduced at high pH

    Faster decomposition above pH 8

    GB BPR Status

    Transitional Supply

    ChloroKlean: applicable in-situ precursor route and stated PT5/PT11 uses

    Check Each Product

    Verify authorisation or applicable transitional status by route and product type

    When to Choose Each

    Choose Chlorine Dioxide When:

    • You need a measurable residual across long pipe runs
    • Biofilm control in cooling tower fill packs is essential
    • Source water contains bromide and you need to avoid bromate
    • Capital budget rules out an on-site ozone generator
    • ACoP L8 / HSG274 compliance with continuous biocide is required
    • Multiple distributed dosing points need simple, reliable injection

    Consider Ozone When:

    • Single point-of-dose application with no distribution network
    • Removal of taste, odour, and colour at a treatment works
    • High organic load requiring strong oxidation before filtration
    • Capital budget for a generator and contactor is available
    • A secondary residual disinfectant is already in place downstream

    Why Choose ChloroKlean Plus L20

    If you're considering switching to chlorine dioxide, ChloroKlean Plus L20 is purpose-built for industrial and commercial applications.

    Supplied for GB PT5 / PT11 Uses

    ChloroKlean Plus L20 is supplied in Great Britain under transitional arrangements for the applicable in-situ precursor route and its stated PT5 and PT11 uses. This is not a claim of product authorisation; no EU or Northern Ireland authorisation is claimed.

    Regenerative ClO₂ Chemistry

    Stabilised, regenerative formulation delivers sustained antimicrobial action at low doses (0.1-0.5 ppm). No on-site generator, no contactor, no ozone destruction unit.

    Independently Tested

    BS EN 13623:2020 testing confirms >4-log Legionella reduction in cooling water. Documented biofilm penetration in field installations where ozone left residual fouling.

    Regulatory and Scientific References

    This comparison is informed by the following authoritative sources. Always refer to the latest published guidance.

    WHO Guidelines
    World Health Organization (WHO)

    Guidelines for Drinking-water Quality: Chlorine Dioxide

    WHO describes chlorine dioxide use and the need to control its chlorite and chlorate by-products.

    View source
    HSE HSG274 Part 1
    Health and Safety Executive (HSE)

    Legionnaires' disease: Technical guidance for cooling towers

    HSG274 Part 1 sets out the technical requirements for biocide selection and residual maintenance in cooling tower systems.

    View source
    US EPA D/DBPR
    US Environmental Protection Agency

    Stage 1 and Stage 2 Disinfectants and Disinfection Byproducts Rules

    EPA D/DBPR sets limits on bromate (10 µg/L) and other regulated by-products formed during ozonation of bromide-containing source water.

    View source
    DWI Guidance
    Drinking Water Inspectorate (DWI)

    List of approved products and chemicals for use in public water supply

    For public water supply in England and Wales, DWI Regulation 31 approval and its conditions apply to the specific product and use. That approval is separate from GB BPR product authorisation or transitional status and does not imply approval of ChloroKlean.

    View source
    EU BPR 528/2012
    European Parliament and Council

    Biocidal Products Regulation

    EU BPR applies in the EU and Northern Ireland. Great Britain has a separate GB BPR regime, where status must be checked by product, product type and active-substance precursor route; applicable transitional supply is distinct from product authorisation.

    View source
    HSE GB Review Programme
    Health and Safety Executive (GB BPR)

    GB Review Programme for existing biocidal active substances

    HSE explains the transitional arrangements that may permit continued supply while an existing active-substance precursor route and product-type combination is under review.

    View source
    HSE GB Article 95
    Health and Safety Executive (GB BPR)

    GB Article 95: the basics

    HSE explains the GB Article 95 active-substance supply-chain requirement. Article 95 evidence does not establish finished-product authorisation.

    View source

    Frequently Asked Questions

    Ozone has a higher oxidation potential than chlorine dioxide (2.07 V vs 0.95 V), so it reacts faster at the point of dosing. However, ozone has no residual and a half-life of around 20 minutes in water, so it cannot maintain protection across a distribution system. Chlorine dioxide provides sustained biocidal action and a measurable residual, which is usually more important for cooling towers and drinking water networks under HSG274.

    Yes. Ozone oxidises naturally occurring bromide in source water to bromate, a regulated disinfection by-product. The US EPA limit is 10 µg/L. Chlorine dioxide does not oxidise bromide to bromate, so it is preferred where source water bromide is elevated or where bromate compliance is marginal.

    Cooling towers under HSG274 and ACoP L8 require a measurable biocide residual throughout the recirculating system, including the fill packs and basin where biofilm forms. Ozone is consumed too quickly to provide that residual, and is rarely cost-effective at typical cooling tower volumes. Chlorine dioxide penetrates biofilm in the fill, maintains residual, and dosing equipment is far simpler than ozone generation. See ChloroKlean for cooling towers.

    Yes, in most cooling tower and distributed water applications. Chlorine dioxide dosing uses a simple metering pump and storage tank instead of an ozone generator, contactor, and destruction unit. The transition usually involves draining and cleaning the system, then commissioning a ClO₂ dosing rig sized to maintain 0.1 to 0.5 ppm residual. ChloroKlean's technical team can specify equipment and dosing for the changeover.

    There is no blanket UK approval for chlorine dioxide or every chlorine dioxide product. For public water supply in England and Wales, the specific product and use must meet applicable Drinking Water Inspectorate Regulation 31 requirements and conditions; Scotland and Northern Ireland have equivalent but separate regimes. For GB BPR, verify one of two routes. For an authorised product, obtain its GB authorisation number and check the authorised uses and conditions. For transitional supply, obtain evidence that the specific active-substance precursor route and PT5 combination remains covered by the GB Review Programme, check applicable deadlines and the product label, and verify the GB Article 95 supply chain. Article 95 evidence is not product authorisation. ChloroKlean is supplied in Great Britain under transitional arrangements for its stated PT5 uses; no EU or Northern Ireland authorisation is claimed.

    No. Ozone decomposes rapidly in water with a half-life of around 20 minutes, depending on pH and temperature. It leaves no measurable disinfectant residual, which is why systems using ozone almost always require secondary disinfection with chlorine, chloramine, or chlorine dioxide downstream of the ozone contactor.

    Replace Ozone with a Simpler GB-Supplied Alternative

    ChloroKlean Plus L20 is supplied in Great Britain under GB BPR transitional arrangements for its stated PT5 and PT11 uses, providing residual chlorine dioxide without the capital cost or complexity of an ozone generator.