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How is Legionella risk controlled in water lines?

Legionella multiplies in stagnant, warm water conditions, especially within biofilm; hot-water plumbing, cooling towers and rarely used lines are the main risk points. The key to control is suppressing biofilm. Continuous low-dose hypochlorous acid, thanks to its biofilm-penetrating property, provides more stable control than intermittent shock chlorination.

Legionella is a bacterium that can be present in water systems and can cause serious infection through inhalation. Managing the risk begins with understanding where and why the bacterium grows.

Where does Legionella grow?

The ideal conditions for Legionella are quite specific:

  • Temperature: the 20–45°C range is the most favourable for growth. That is why the warm zones of hot-water plumbing and cooling circuits are critical points.
  • Stagnation: dead legs where water waits, rarely used taps and reservoirs create risk.
  • Biofilm: the most important factor. Legionella shelters and multiplies within the biofilm layer on the inner pipe surface.

When these three factors come together — a warm, stagnant, biofilm-laden line — the risk reaches its highest level.

Why is biofilm so important?

Biofilm is a protective layer formed by microorganisms attaching to the pipe surface. For Legionella it is both a shelter and a food source. More importantly, biofilm physically protects the bacterium from disinfectants.

This explains the core challenge in Legionella control: killing free bacteria in the water is easy, but reaching the bacteria within the biofilm is hard. An effective control strategy must be able to penetrate the biofilm layer.

The limit of shock chlorination

A common method is periodic shock chlorination: a high dose of chlorine is delivered to the line to reduce the load. This is momentarily effective, but biofilm re-forms quickly and the risk accumulates again until the next shock. Intermittent intervention is a structurally weak solution to a problem that requires continuity.

The advantage of continuous disinfection

The uncharged, small molecular structure of hypochlorous acid enables it to penetrate the biofilm layer. When continuous low-dose hypochlorous acid is delivered to hot and cold water lines, the re-growth of biofilm is suppressed; instead of spiking intermittently, the risk is held stably low.

The practical advantages of this approach:

  • Biofilm growth is continuously suppressed, preventing intermittent re-accumulation.
  • Dosing is continuously monitored; control becomes measurable and documentable.
  • The same generation unit feeds both the water line and — where needed — surface disinfection.

A holistic approach

Legionella control is not the job of a single device; it is the combined execution of temperature management, elimination of dead legs, regular monitoring and effective disinfection. Continuous hypochlorous acid dosing is one of the most critical and most measurable components of that whole. For healthcare facilities, hotels and large facility water systems, this approach makes the risk manageable and documentable.

What the guidance says

The World Health Organization’s dedicated guidance builds Legionella risk management not on spot sampling but on a water safety plan covering the building’s water system as a whole. It sets out a framework for assessing and managing hazardous environments including cooling towers, pools and spa baths, and foregrounds temperature control, elimination of dead legs and a continuous disinfectant residual as the core measures.1

What those three measures have in common matters: none of them is “raise the dose”. All three work by removing the conditions in which the bacterium can multiply.

Why a sample result alone is not enough

Legionella lives not in the water itself but in the biofilm on the pipe wall. That distinction has a measured counterpart.

LeChevallier and colleagues measured surface-attached biofilm bacteria as 150 to more than 3,000 times more resistant to hypochlorous acid than free-floating cells. The same study showed that for free chlorine the rate-limiting factor is transport of disinfectant into the biofilm — and that consequently, raising the chlorine level does not raise disinfection efficiency.2

In a second study the same team identified what allows bacteria to survive chlorination in distribution systems: surface attachment, shelter inside particles, and adaptation following earlier exposure.3

For an operator the conclusion is clear: a normal-looking free-chlorine residual is not proof that a line is microbiologically clean.

pH is in play here too

How much of the chlorine dosed into a line is in the active form is a separate variable. The US Environmental Protection Agency’s CT tables show that at 10 °C and 1.0 mg/L free chlorine, 3-log inactivation requires 79 mg·min/L at pH 6, 162 at pH 8 and 234 at pH 9.4

In a high-pH hot water circuit, then, two disadvantages compound: a smaller share of the chlorine is in the active form, and reaching the biofilm with that share is already limited. This is why a disinfectant generated at neutral pH makes a difference in these circuits.

References

The peer-reviewed studies and official guidance documents cited in this article. Every citation has been verified against the primary record.

  1. World Health Organization (2007). Legionella and the Prevention of Legionellosis. WHO, Geneva.

    What this source establishes: The WHO guidance establishing that Legionella risk is managed through a building-wide water safety plan rather than one-off sampling. It names temperature control, elimination of dead legs and a continuous disinfectant residual as the core measures.

  2. LeChevallier, M. W., Cawthon, C. D., Lee, R. G. (1988). Inactivation of Biofilm Bacteria. Applied and Environmental Microbiology, 54(10), 2492–2499.

    What this source establishes: Surface-attached biofilm bacteria proved 150 to more than 3,000 times more resistant to hypochlorous acid than unattached cells. The study also showed that transport of disinfectant into the biofilm is the rate-limiting factor — which is why raising the chlorine dose does not raise efficiency.

  3. LeChevallier, M. W., Cawthon, C. D., Lee, R. G. (1988). Factors Promoting Survival of Bacteria in Chlorinated Water Supplies. Applied and Environmental Microbiology, 54(3), 649–654.

    What this source establishes: Identifies what lets bacteria survive chlorination in distribution systems — surface attachment, shelter inside particles, and adaptation from prior exposure. It shows that a measured free-chlorine residual alone does not guarantee microbiological safety.

  4. U.S. Environmental Protection Agency (2003). LT1ESWTR Disinfection Profiling and Benchmarking Technical Guidance Manual — Appendix B: CT Tables. EPA Office of Water, EPA 816-R-03-004.

    What this source establishes: The official CT (concentration × contact time) tables for free chlorine. At 10 °C and 1.0 mg/L, 3-log Giardia inactivation requires 79 mg·min/L at pH 6, 162 at pH 8 and 234 at pH 9 — the required dose doubles to triples on pH alone.

SSS

Frequently asked questions

Where does Legionella grow most?

In stagnant water in the 20–45°C range and within biofilm. Hot-water plumbing, cooling towers, decorative water features and long-unused lines are the main risk points.

Isn't shock chlorination enough?

Shock chlorination lowers the load momentarily, but biofilm can re-form quickly. Continuous low-dose disinfection provides more stable control by suppressing the re-growth of biofilm.

Let's discuss how it works in practice.

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