A water filter can claim:
“Removes up to 99% of contaminants.”
That sounds impressive.
But there is a problem with looking at the number alone.
A filter does not work in empty water.
It works in real water.
Real water contains minerals, organic matter, salts and many other substances. These can change how a filter performs.
That is why the same filter can perform differently in different water sources.
The key question is not only:
“What can this filter remove?”
It is also:
“How does this filter perform in this particular water?”
A filter does not treat every water sample the same way
Imagine two water samples.
Both contain the same target contaminant.
The first contains very little else.
The second contains:
- calcium
- magnesium
- dissolved organic matter
- other contaminants
- different levels of salts
The filter now faces two very different conditions.
The target contaminant may interact with the filter medium differently in each sample.
This is particularly important for adsorption-based filtration, where contaminants attach to surfaces within the filter medium. The EPA identifies pH, contaminant properties, water chemistry and competing substances as factors that can affect adsorptive treatment. US EPA
What does “water chemistry” actually mean?
Water chemistry is simply the chemical composition of the water.
It can include:
- pH
- dissolved minerals
- salts
- organic matter
- metals
- gases
- dissolved contaminants
These properties are not independent.
They interact with each other.
And they can also interact with the filter medium.
That is why water treatment is more complex than putting a material in a cartridge and measuring one removal percentage.
pH can change filter performance
One of the most important variables is pH.
pH affects the chemical form and charge of some substances.
It can also change the surface properties of certain filter media.
As a result, a contaminant may interact more strongly or more weakly with a filter depending on the water’s pH.
The EPA specifically lists pH as an important factor for adsorptive media used to remove inorganic contaminants. US EPA
So a statement such as:
“This medium removes X.”
is incomplete without knowing the conditions under which that performance was measured.
Minerals matter too
Calcium and magnesium are common in drinking water.
They are not automatically unwanted contaminants.
But they contribute to the overall water chemistry.
Other dissolved ions can also affect interactions between contaminants and filter surfaces.
In some systems, changes in ionic strength or the presence of competing ions can influence adsorption.
PFAS are a good example.
Research reviewed by the EPA shows that geochemical conditions and competing ions can affect PFAS adsorption to different surfaces. nepis.epa.gov
So even when the target contaminant stays the same, the surrounding water can change the treatment conditions.
Natural organic matter can compete with contaminants
This is one of the most important points.
Natural water often contains natural organic matter, or NOM.
It comes from sources such as:
- soil
- plants
- decaying organic material
- surface water
Activated carbon can adsorb some of this organic matter.
That means NOM can occupy adsorption sites that could otherwise interact with a target contaminant.
The EPA identifies competition from natural organic matter as a factor that can reduce adsorption performance for some contaminants. US EPA
In simple terms:
The filter does not know which molecule your marketing claim is about.
It interacts with everything in the water.
PFAS show why this matters
PFAS treatment is a good example of why laboratory numbers need context.
Activated carbon can remove many PFAS from water.
But performance depends on several factors.
These include:
- the type of PFAS
- carbon type
- contact time
- flow rate
- temperature
- organic matter
- other substances in the water
The EPA notes that activated carbon generally performs better for longer-chain PFAS than for shorter-chain PFAS. It also identifies flow rate, temperature and organic matter as factors affecting performance. US EPA
So:
“99% PFAS removal” is not a complete description of a treatment system.
You need to know:
99% of which PFAS?
At what concentration?
In what water?
At what flow rate?
For how long?
One PFAS is not the same as another
PFAS are a large group of different substances.
They do not all interact with filter media in the same way.
Longer-chain PFAS often adsorb more strongly to activated carbon than shorter-chain PFAS.
Short-chain PFAS can be more difficult for conventional activated carbon to capture. US EPA
That means a filter test using one PFAS cannot automatically be used to predict its performance for every PFAS.
This is a common problem with broad marketing statements.
A result for one substance is not automatically a result for an entire chemical class.
Flow rate changes the conditions
Water does not simply sit inside a filter.
It flows through it.
The faster the water moves, the less time it may have to interact with the filter medium.
This is especially relevant for adsorption.
The EPA identifies water loading rate and empty bed contact time as important factors in granular activated carbon treatment. US EPA
Therefore, a filter tested at one flow rate should not automatically be expected to deliver exactly the same performance at a much higher flow rate.
This is why capacity and flow rate belong together.
Contact time matters
Consider two identical filters.
The first treats water slowly.
The second treats water much faster.
Even though the filter media are identical, the water spends different amounts of time interacting with the media.
That can change treatment performance.
This is particularly important for adsorption-based systems.
The EPA’s guidance on activated carbon specifically links performance to factors such as contact time and loading rate. US EPA
So a filter’s physical size alone does not tell you everything about its treatment performance.
Temperature can matter
Water temperature can also influence treatment processes.
For some adsorption systems, temperature affects the interaction between contaminants and the filter medium.
The effect is not identical for every contaminant or technology.
That is the important point:
There is no single “temperature effect” that applies to every filter.
Instead, temperature is one of several operating conditions that can influence performance.
Concentration matters
Imagine a filter is exposed to:
1 µg/L
of a contaminant.
Now imagine the same filter receives:
100 µg/L.
The filter is dealing with a much larger contaminant load.
Its treatment capacity will therefore be consumed differently.
This is why a filter’s capacity cannot be separated from the concentration of the substances entering the system.
A removal percentage without the starting concentration tells only part of the story.
“Up to 99%” needs context
This is where marketing language can become misleading.
“Up to 99% removal” may be a legitimate test result.
But it does not necessarily mean:
99% removal for every contaminant
or
99% removal for the entire lifetime of the filter.
The number may apply to:
- one specific contaminant
- one specific concentration
- one specific water matrix
- one flow rate
- one temperature
- one filter configuration
- one test duration
A strong technical claim should therefore always come with its test conditions.
Laboratory water is not always real-world water
Laboratory testing is essential.
It allows researchers and manufacturers to control conditions and compare results.
But controlled water can be much simpler than real drinking water.
Real water contains mixtures.
Those mixtures can interact.
For example, natural organic matter can compete with target contaminants for adsorption sites. HERO
This is why performance testing in representative water is so valuable.
The closer the test conditions are to the intended application, the more useful the result becomes for real-world system design.
The same filter can behave differently in two locations
Consider two buildings.
Both use the same filter.
But the water entering each building has a different composition.
One source may contain more:
- calcium
- magnesium
- organic matter
The other may have a different mineral balance and a different contaminant profile.
The filter itself has not changed.
The water has.
Therefore, the treatment conditions have changed too.
This is why filter selection should start with understanding the water.
Water chemistry can also affect filter lifetime
Filter performance is not only about removal efficiency.
It is also about how long that performance lasts.
If other substances occupy adsorption sites, the filter can reach its effective capacity sooner.
High concentrations of organic matter can therefore increase the treatment burden on activated carbon. The EPA notes that high organic concentrations and high flow rates can lead to more frequent media replacement. US EPA
So the question is not only:
“Can this filter remove the contaminant?”
It is also:
“How long can it keep doing so under these conditions?”
Selectivity is important
A good treatment system does not necessarily need to remove everything.
In many applications, the goal is more specific.
For example:
reduce a target contaminant
while
preserving desirable minerals
and
maintaining a suitable taste
That requires selectivity.
Modern adsorptive media can be designed around specific interactions between contaminants and surfaces.
The EPA recognises a range of adsorptive media beyond activated carbon, including media based on aluminium, iron, titanium and zirconium. Their performance depends on the specific medium and water chemistry. US EPA
This is one reason there is no universal “best filter.”
A filter is not a standalone product
A filter should be viewed as part of a system.
Its performance depends on:
Water
Filter medium
Flow
Contact time
Operating conditions
Maintenance
Change one of these, and the result can change.
That is why professional water treatment starts with the application rather than the product name.
What should you ask before choosing a filter?
Instead of asking only:
“What does this filter remove?”
ask these questions:
1. Which contaminants were tested?
A specific substance or a broad group?
2. At what concentration?
A low concentration and a high concentration can create different treatment demands.
3. In what water?
Was it laboratory water or representative source water?
4. At what flow rate?
Was the test performed under realistic operating conditions?
5. For how long?
Was the result measured initially or over an extended operating period?
6. What happens at capacity?
Does performance decline gradually or is there a defined breakthrough point?
7. What does the filter retain?
Does the contaminant stay in the medium, move into another waste stream or require regeneration?
These questions reveal much more than a single percentage.
This does not mean filter claims are useless
Quite the opposite.
A good test result is valuable.
The problem is using a test result outside the conditions under which it was generated.
A properly documented removal claim can tell you a lot.
But it should answer:
What was tested?
How was it tested?
Under which conditions?
For how long?
That is the difference between a meaningful performance claim and a number without context.
What this means for modern filtration
The future of water treatment is moving toward more targeted solutions.
Instead of asking:
“How can we remove as much as possible?”
a better question is:
“How can we target the substances that matter under the actual conditions of the water?”
That requires understanding the chemistry of both sides:
the water
and
the filter surface.
This is particularly important for complex water containing mixtures of dissolved substances.
The Klar2O perspective
Klar2O’s approach to filtration is based on this broader idea.
Its Smart Surface Technology uses biochemically coated silica beads designed to interact with target contaminants through adsorption rather than relying only on physical pore size. [Klar2O, Our Solution, https://klar2o.com/about-us]
That distinction matters because dissolved contaminants cannot simply be treated like particles passing through a sieve.
Their removal depends on the interaction between:
contaminant
water chemistry
and
filter surface.
The goal is therefore not simply to make a filter as fine as possible.
It is to make the interaction more targeted and effective.
The bottom line
A filter does not operate in isolation.
Water chemistry affects how contaminants behave.
And it can affect how they interact with a filter.
pH, minerals, organic matter, contaminant concentration, flow rate and contact time can all influence treatment performance. US EPA
That is why a marketing claim such as:
“Removes 99%”
should always lead to another question:
“Under which conditions?”
The best filter is not necessarily the one with the biggest number on the package.
It is the one whose performance has been demonstrated for the right contaminant, in the right water, under the right operating conditions.
Water chemistry comes first. The filter comes second.