Catalytic filter media — manganese-dioxide-coated greensand and modern equivalents that catalyse and capture iron and manganese in one bed.
Iron & Manganese Removal — in depth
Catalytic media solve the slow-manganese problem. Manganese-dioxide-coated greensand (and modern pyrolusite-type media) catalyse the oxidation of iron and manganese at the grain surface and filter the product in a single bed — regenerated continuously by a trace oxidant or periodically by permanganate, giving reliable manganese removal in a compact pressure filter.
What matters in practice
Catalyses Fe/Mn oxidation at the surface.
Overcomes slow Mn kinetics.
Continuous or intermittent oxidant.
Oxidation and filtration together.
| Media | Action | Regeneration |
|---|---|---|
| Greensand | Catalytic | KMnO₂ |
| Pyrolusite | Catalytic | Chlorine |
| Bed | Pressure filter | Compact |
| Mn | Reliable | Catalysed |
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Fundamentals, design drivers and practical guidance
Catalytic filter media — manganese-dioxide-coated greensand and modern equivalents that catalyse and capture iron and manganese in one bed.
Borehole and groundwater supplies are chemically reducing, often free of oxygen, and characteristically carry dissolved iron and manganese, sometimes arsenic, fluoride, ammonia or hydrogen sulphide. Because the raw water is clear at the wellhead and only discolours after contact with air, treatment is designed around controlled oxidation followed by filtration — converting dissolved metals into a filterable floc before they reach the distribution network.
Iron and manganese removal is governed by oxidation kinetics and pH. Iron oxidises readily by aeration above pH 7; manganese is far slower and usually needs a higher pH, a stronger oxidant, or a catalytic filter media that adsorbs and auto-catalyses the reaction. Where biological iron and manganese removal is used, naturally occurring bacteria perform the oxidation within the filter at lower chemical dose, producing a compact, backwashable bed.
Arsenic and fluoride demand specific chemistry: arsenic is best removed after oxidising As(III) to As(V) followed by adsorption or co-precipitation onto iron oxides, while fluoride responds to activated alumina or bone-char adsorption. Continuous water-quality monitoring at the wellhead and post-filter closes the loop, confirming that breakthrough is detected before it reaches consumers and that backwash is triggered on differential pressure or run-time.
What our engineers assess on every scope of this type
| Parameter | Typical basis | Why it matters |
|---|---|---|
| Arsenic | Oxidise then adsorb on Fe oxide | As(V) removes far better than As(III) |
| Fluoride | Activated alumina / bone char | Adsorption to meet drinking limit |
| Media | Catalytic or biological | Sets dose and backwash regime |
| Monitoring | Wellhead + post-filter | Detects breakthrough before supply |
| Iron (Fe) | Aeration > pH 7 | Oxidises fast to filterable floc |
| Manganese (Mn) | High pH / oxidant / catalytic media | Slow kinetics; needs help |
Common questions on borehole water treatment
Backwash is initiated on accumulated differential pressure, treated-water turbidity, or elapsed run-time — whichever comes first. This keeps the bed clean and the oxidised solids out of supply.
Yes — biological iron and manganese removal uses naturally occurring bacteria within the filter to oxidise the metals at reduced chemical dose, giving a compact, robust bed where the groundwater chemistry suits it.
Because dissolved iron (and manganese) are invisible in the reducing groundwater but oxidise on contact with air, forming coloured particulate. Catalytic Media (Greensand) is designed to oxidise and filter these metals deliberately, before the water reaches the network.
Manganese oxidation is kinetically slow and needs a higher pH, a stronger oxidant or a catalytic media that auto-catalyses the reaction. Sizing a filter on iron alone will leave manganese breaking through, which is why Catalytic Media (Greensand) is sized on manganese kinetics.
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