COD Decoding: Understanding What Is Really in Sewage

Why COD is not just a number—and why decoding it changes how STPs should be designed
Why COD Needs to Be “Decoded”
COD fractionation infographic showing rbCOD, sbCOD, particulate biodegradable COD and inert COD, explaining which organics react quickly, slowly, or do not biodegrade in sewage treatment.
COD fractionation infographic showing rbCOD, sbCOD, particulate biodegradable COD and inert COD, explaining which organics react quickly, slowly, or do not biodegrade in sewage treatment.
COD fractionation infographic showing rbCOD, sbCOD, particulate biodegradable COD and inert COD, explaining which organics react quickly, slowly, or do not biodegrade in sewage treatment.

In many sewage treatment plant (STP) designs, Chemical Oxygen Demand (COD) is treated as a single value—reported, checked, and sometimes compared against limits prescribed by the Central Pollution Control Board (CPCB).

Yet in practice, engineers and operators often observe that:

  • COD remains high even when BOD is low

  • Longer aeration does not reduce COD further

  • Nitrogen removal is inconsistent despite “adequate” treatment

These observations point to a simple but often ignored reality:

COD is not a single type of organic matter.
It is a mixture of very different fractions, each behaving differently in biology.

Understanding COD therefore requires decoding it.

What COD Actually Represents

COD measures the total oxygen demand of organic matter in wastewater—both biodegradable and non-biodegradable—using a chemical test.

Unlike BOD, COD:

  • Captures fast and slow reacting organics

  • Includes particulate and soluble matter

  • Includes organics that biology can never remove

COD therefore gives a more complete picture of what is present in sewage.

But by itself, a total COD number still does not explain how treatment will behave.

COD Is a Combination of Different Fractions

To be meaningful for design, COD must be viewed as a set of fractions, not a single value.

Broadly, COD consists of:

Readily biodegradable COD (rbCOD)
  • Organic matter that microorganisms can consume almost immediately.

Soluble biodegradable COD (sbCOD)
  • Organic matter that reacts biologically, but more slowly.

Particulate biodegradable COD
  • Organic matter must first undergo hydrolysis before it can be used by biology.

Inert COD (soluble and particulate)
  • Organic matter that does not degrade biologically at all.

Each of these fractions:

  • Exerts oxygen demand at a different time

  • Contributes differently to treatment performance

  • Responds differently to aeration and retention time

Today, these assumptions no longer hold.

Why Total COD Alone Is Misleading

Two wastewaters can have the same COD value and still behave very differently inside an STP.

For example:

  • One may be rich in rbCOD and react quickly

  • Another may be dominated by particulate or inert COD and react slowly—or not at all

If design is based only on total COD:

  • Aeration may be applied too early or too late

  • Biological reactions may be incomplete

  • Energy may be consumed without proportional treatment benefit

This is why COD decoding is more important than COD measurement alone.

The Role of Hydrolysis in COD Behaviour
Hydrolysis reaction in sewage showing particulate organic matter converting into soluble molecules, turning slowly biodegradable COD into readily biodegradable BOD for improved STP biological treatment.
Hydrolysis reaction in sewage showing particulate organic matter converting into soluble molecules, turning slowly biodegradable COD into readily biodegradable BOD for improved STP biological treatment.
Hydrolysis reaction in sewage showing particulate organic matter converting into soluble molecules, turning slowly biodegradable COD into readily biodegradable BOD for improved STP biological treatment.

A large fraction of sewage COD is particulate.

Before biology can oxidise it, this particulate COD must be converted into soluble form through hydrolysis.

Hydrolysis:
  • Is a biological, enzyme-driven process

  • Takes time

  • Cannot be accelerated by increasing aeration

If hydrolysis has not occurred:
  • Oxygen remains unused

  • COD removal plateaus

  • Extended aeration shows little benefit

This explains why some STPs appear “under-treated” even with long aeration durations.

👉 This links directly to:

Inert COD: The Invisible Limitation

Inert COD is often the most misunderstood fraction.

Key Characteristics:
  • It does not degrade biologically

  • It passes through biological reactors unchanged

  • It accumulates in sludge over time

No amount of:
  • Aeration

  • Retention time

  • Biological optimisation

can remove inert COD.

Designs that assume all COD is removable inevitably:
  • Overestimate achievable performance

  • Create unrealistic expectations

  • Lead to long-term operational stress

Recognising inert COD is essential for realistic design and compliance planning.

Why COD Decoding Matters for Nutrient Removal
Infographic showing influence of COD on nitrification and denitrification, where hydrolysis increases carbon availability and enables denitrification without oxygen while nitrification requires oxygen.
Infographic showing influence of COD on nitrification and denitrification, where hydrolysis increases carbon availability and enables denitrification without oxygen while nitrification requires oxygen.
Infographic showing influence of COD on nitrification and denitrification, where hydrolysis increases carbon availability and enables denitrification without oxygen while nitrification requires oxygen.

Biological nitrogen removal depends on:

  • Availability of biodegradable carbon

  • Carbon being available at the right time

Total COD does not indicate whether:

  • Sufficient rbCOD is present for denitrification

  • Carbon will be available during anoxic phases

This is why many STPs:

  • Achieve ammonia removal

  • But struggle with total nitrogen

COD decoding helps identify whether the right type of carbon exists to support nutrient removal—without relying on trial-and-error operation.

How COD Decoding Improves Design Decisions

When COD is decoded at the design stage, engineers can:

  • Align aeration with actual oxygen demand

  • Design for reaction timing, not averages

  • Set realistic expectations for COD and nutrient removal

  • Avoid over-sizing blowers and reactors

  • Improve long-term stability and energy efficiency

In short, COD decoding transforms STP design from assumption-based to behaviour-based.

Conclusion

COD is often measured, reported, and discussed—but rarely understood.

Treating COD as a single number hides:

  • Reaction timing differences

  • Hydrolysis limitations

  • Inert organic fractions

Decoding COD reveals how sewage will actually behave inside a treatment system. Only with this understanding can STPs be designed for stable, efficient, and predictable performance.