How does electrochemical activation (ECA) work?
Electrochemical activation (ECA) is the process of passing a dilute brine solution through an electrolysis cell to convert it into a disinfectant solution dominated by hypochlorous acid; in a diaphragm cell, the cathode side also yields sodium hydroxide (caustic) as a second, usable output. The only inputs are salt, water and electricity; the result is fresh disinfectant produced where it is needed, with no hazardous chemical transport or storage.
In this article
Electrochemical activation is a technology that looks complex but has extremely simple inputs: salt, water and electricity. A powerful disinfectant is produced from these three inputs, and no other chemical is required.
The basic principle: electrolysis
At the heart of the system is an electrolysis cell. A dilute salt (sodium chloride) solution is passed through this cell. When electricity is applied to the electrodes inside the cell, the water and salt molecules enter electrochemical reactions.
The chloride ions in the solution are oxidised at the anode and react with water to form hypochlorous acid (HOCl). The result is a solution with a low salt concentration but a high disinfecting power. At the cathode, water is reduced to hydrogen and hydroxide ions; together with the sodium ions in the solution, this forms sodium hydroxide (NaOH).
Diaphragm and non-diaphragm cells
ECA cells can be of two main types:
- Non-diaphragm (single cell): The anode and cathode are in the same chamber, so the products of both electrodes mix into a single solution.
- Diaphragm: The anode and cathode chambers are separated by a diaphragm, producing two distinct solutions: a hypochlorous acid-dominant oxidant (anolyte) on the anode side and a sodium hydroxide solution (catholyte) on the cathode side.
The Aquamirus E.C.A. system uses a diaphragm cell. Keeping the two products apart means the anolyte is not pushed toward the weaker hypochlorite form by hydroxide from the cathode, and the facility gains a second output: caustic that can be used on site for alkaline cleaning, CIP or pH correction, rather than being treated as waste.
Production to demand
The most important operating feature of ECA systems is that they can run to demand. The system starts and stops production automatically based on the free-chlorine measurement on the dosed line. As a result:
- Overproduction and over-dosing are prevented.
- The solution is always used fresh, with no shelf-life problem.
- Dosing is matched to the facility’s real-time need.
Why on-site generation?
In the traditional method, disinfectant (for example sodium hypochlorite) is bought in drums, transported and stored. This chain brings several problems: hazardous-goods transport and storage requirements, loss of efficacy over time, and continual supply dependency.
On-site generation removes this chain. The facility produces its own disinfectant, keeping only salt as an input alongside electricity. This makes a clear difference to both safety and operating cost.
Where is it used?
ECA technology is used today across a broad range — from drinking-water networks to swimming pools, food-processing plants to healthcare facilities, agricultural irrigation to livestock. The common thread is always the same: the need for safe, effective and continuous disinfection.
What actually governs efficacy: redox potential
The strength of an ECA solution is usually described with a single number — free chlorine concentration. Measurements show the picture is more complicated.
Kim, Hung and Brackett separated the variables behind electrolyzed oxidizing water’s efficacy: pH, oxidation–reduction potential (ORP) and residual chlorine. By comparing against chemically modified solutions engineered to share properties with EO water, they assessed each variable’s contribution to inactivation independently. ORP emerged as the governing variable.1
For an operator that means redox potential is not a derived indicator of free chlorine but a process parameter to be monitored in its own right. It is why the Aquamirus E.C.A. system measures and reports ORP independently.
Why pH matters this much
How much of the chlorine generated at the anode remains in the active hypochlorous acid form is set by the water’s pH. The dissociation constant describing that equilibrium was measured in 1948: pKa ≈ 7.5.3
The practical consequence: at pH 6 roughly 97% of free chlorine is in the active form; at pH 8 that falls to 26%, and at pH 9 to 3%. This is why cell design matters: in a diaphragm cell the hydroxide formed at the cathode stays out of the anolyte, so the anode-side solution remains in the range where hypochlorous acid dominates.
Measured effect on viruses
The efficacy of electrolyzed water is not limited to bacteria. Tamaki and colleagues tested neutral electrolyzed water against avian influenza viruses.
The finding: with the solution at 43 ppm free available chlorine or above, the titre of highly pathogenic H5N1 and low-pathogenic H9N2 fell by more than 5 log within 1 minute, irreversibly. At free chlorine below 17 ppm the effect was absent; the minimum threshold for a virucidal effect was estimated at about 40 ppm.4
A notable detail from the same study: no viral gene fragments could be amplified from virus inactivated by the neutral solution — the effect is structural disintegration, not a superficial loss of activity.
The method’s standing in industry
Industrial use of electrolyzed water has been reviewed in the peer-reviewed literature. A review focused on the food industry records that the method’s only chemical input is salt, that generation can take place at the point of use, and that it offers cost and environmental advantages over conventional systems.2
References
The peer-reviewed studies and official guidance documents cited in this article. Every citation has been verified against the primary record.
(2000). Roles of Oxidation–Reduction Potential in Electrolyzed Oxidizing and Chemically Modified Water for the Inactivation of Food-Related Pathogens. Journal of Food Protection, 63(1), 19–24.
What this source establishes: Separates out the variables behind electrolyzed oxidizing water’s efficacy and shows oxidation–reduction potential (ORP) — more than pH or residual chlorine — governs inactivation. This is the basis for monitoring redox potential as an independent process parameter.
Open source ↗ PMID 10643764
(2016). Electrolyzed Water as a Novel Sanitizer in the Food Industry: Current Trends and Future Perspectives. Comprehensive Reviews in Food Science and Food Safety, 15(3), 471–490.
What this source establishes: A peer-reviewed review of electrolyzed water across the food industry. It concludes that the only chemical input is salt, that generation can happen at the point of use, and that the method offers cost and environmental advantages over conventional cleaning systems.
Open source ↗ DOI 10.1111/1541-4337.12200PMID 33401818
(1948). The Behavior of Chlorine as a Water Disinfectant. Journal AWWA, 40(10), 1051–1061.
What this source establishes: The foundational study describing the HOCl ⇌ OCl⁻ equilibrium in water and how pH shifts it. Its dissociation constant (pKa ≈ 7.5) is what makes it possible to calculate how much of a free-chlorine residual is actually in the active form.
Open source ↗ DOI 10.1002/j.1551-8833.1948.tb15055.x
(2014). Virucidal Effect of Acidic Electrolyzed Water and Neutral Electrolyzed Water on Avian Influenza Viruses. Archives of Virology, 159(3), 405–412.
What this source establishes: Neutral electrolyzed water containing ≥43 ppm free available chlorine irreversibly reduced the titre of highly pathogenic H5N1 and low-pathogenic H9N2 avian influenza virus by more than 5 log within 1 minute; the minimum free chlorine for a virucidal effect was estimated at about 40 ppm.
Open source ↗ DOI 10.1007/s00705-013-1840-2PMID 24026292