Effluent discharge limits across Africa
The number your plant has to hit is set by law, not by a supplier. This is an open reference to what each African jurisdiction actually requires — traced to the instrument, dated, and rechecked.
Every limit published here is traced to the primary legal instrument that sets it, and carries two dates: when the instrument was made, and when we last checked it against the source. Nothing is published from a secondary summary, a consultant’s slide or another supplier’s website.
That is a slower way to build a reference and it is the only defensible one. A wrong discharge limit is not a typo — it is a plant sized to the wrong target, or a compliance position argued on a figure that does not exist. Countries below are marked verified only when the instrument has been read directly.
Three limits, not one
Almost every African jurisdiction sets different limits depending on where the effluent goes. Quoting “the COD limit” for a country without saying which route is the most common error we see in enquiries, and it changes the treatment plant by a factor of several.
| Discharge route | Typically the | Why | What it means for a DAF |
|---|---|---|---|
| To sewer — into a municipal collection system | Loosest limits | A downstream municipal works will provide biological treatment; the limits exist to protect the sewer, the works and its operators | Often flotation alone is sufficient. FOG and TSS limits dominate; COD limits are generous or absent |
| To surface water — river, lake, sea outfall | Tightest limits | No further treatment follows; the receiving water is the environment | Flotation is a pretreatment stage only. Biological treatment almost always required behind it |
| To land or irrigation reuse | Different, not simply tighter | Salinity, sodium adsorption ratio, chloride and pathogens matter more than COD | Coagulant choice becomes critical — chloride-based products may breach an irrigation limit that a sulphate-based product would not |
And sometimes limits are set by sector, not nationally
A structural point that catches out anyone assuming one national table per country. Nigeria, for example, does not set a single national industrial effluent standard. NESREA issues sector-specific regulations, so a chemicals or detergent plant and a pharmaceutical plant face different numbers for the same parameter — and a food and beverage plant faces a third set again.
Where a country works this way, the country page gives a table per sector rather than one table, and states which regulation applies to which industry. Asking “what is the COD limit in Nigeria” has no single answer, and any source that gives you one has not read the regulations.
The parameters that decide a flotation plant
Discharge consents typically list twenty to forty parameters. Six of them determine whether dissolved air flotation is the right process and how large it needs to be. The rest are usually met or missed elsewhere in the treatment train.
| Parameter | What DAF does to it | Realistic reduction | If the limit is tighter than that |
|---|---|---|---|
| Fats, oils and grease | Removes free and emulsified FOG with correct coagulation | 90–99% | Rarely a problem. FOG is flotation’s strongest duty |
| Total suspended solids | Removes coagulated solids | 85–98% | Add filtration behind the DAF |
| COD | Removes only the particulate fraction | 40–70% where particulate; 20–40% where largely soluble | Biological treatment is required. No coagulant regime substitutes for it |
| BOD₅ | Follows COD — removes the particulate share | 30–60% | Biological treatment required |
| Total phosphorus | Precipitates with an iron or aluminium coagulant | 60–90% | Below about 0.3 mg/L, add a polishing filter. See ferric chloride dosing |
| pH | Changed by the coagulant, not by the flotation | Correctable | Add a pH loop. Note that acidic coagulants consume alkalinity and can breach a lower pH bound |
Verified countries compared
Side by side, for the parameters that decide a flotation plant. Both columns are taken from the primary instrument, not from secondary summaries.
| Parameter | Kenya LN 177/2024, environment | South Africa GN 665/2013, general limit | South Africa GN 665/2013, special limit |
|---|---|---|---|
| COD | 50 mg/L | 75 mg/L | 30 mg/L |
| BODâ‚… | 30 mg/L | Not specified in Table 2.1 | Not specified in Table 2.1 |
| Suspended solids | 30 mg/L | 25 mg/L | 10 mg/L |
| Oil and grease | Nil; n-hexane extracts 30 mg/L fats, 5 mg/L mineral oil | 2.5 mg/L | 0 mg/L |
| pH | 6.5–8.5 non-marine | 5.5–9.5 | 5.5–7.5 |
| Total phosphorus / ortho-P | 2 mg/L total P | 10 mg/L ortho-P | 1 mg/L median, 2.5 max |
| Total nitrogen | 2 mg/L | Ammonia as N 6, nitrate/nitrite as N 15 | Ammonia as N 2, nitrate/nitrite as N 1.5 |
| Dissolved iron | 10 mg/L | 0.3 mg/L | 0.3 mg/L |
| Chloride | 250 mg/L | Not specified; conductivity limited instead | Not specified; conductivity limited instead |
Country coverage
All 54 African countries are listed below. Each is published as its governing instrument is read directly, so a country carries a link only once its schedule has been read line by line. Nothing here is a substitute for the current text of the law, and your local environmental consultant or regulator’s own confirmation takes precedence over this page.
North Africa
West Africa
Central Africa
East Africa
Southern Africa
Countries without a link have not yet had their governing instrument read directly, so no figures are published for them. If you need a specific country prioritised, tell us which and we will move it up the queue.
Why we are not publishing numbers yet
Building this reference began by searching for each country’s standards. Within the first few queries, two things happened that explain the approach above.
- A search for Kenyan effluent standards returned figures that belong to a Mauritian instrument from 2003, presented as though they were Kenyan.
- A second set of Kenyan figures appeared that contradicted the first, with no way to tell from the summaries which schedule either came from — discharge to land and discharge to surface water carry different numbers in the same regulation.
Both are ordinary research errors and both would have been invisible in a published table. That is the problem. A discharge limit is the design basis for a treatment plant and sometimes the basis of a compliance argument with a regulator. Getting it wrong is not an embarrassment to be corrected later; it is a plant built to the wrong specification.
So the rule for this section is simple: a number appears here only after the instrument that sets it has been read directly, and it carries the date it was read. If you need a specific country urgently, say so and we will prioritise it.
Frequently asked questions
What is the COD limit for industrial effluent in Africa?
There is no continental limit. Each country sets its own, and most set different values depending on whether the effluent goes to sewer, to surface water, or to land and irrigation. Several countries — Nigeria among them — set limits per industrial sector rather than nationally, so even within one country there is no single figure. Use this reference to find the instrument that applies to your site and route, then confirm it with the regulator.
Can a DAF alone meet a surface water discharge consent?
For fats, oils and grease and for suspended solids, frequently yes. For COD and BOD against a surface water standard, almost never — flotation removes the particulate fraction of the organic load and cannot touch dissolved organics. On a stream whose COD is largely soluble, such as a brewery, expect 20–40% removal. A DAF ahead of a biological stage is the normal configuration for surface water discharge; a DAF alone is normal for discharge to sewer.
Which limit should I design to if my consent is being renegotiated?
Design to the tighter of the current consent and the national standard, and check whether the standard is under revision. Several African jurisdictions have tightened industrial effluent standards over the last decade, and a plant sized to a consent that expires in three years is a plant that needs rebuilding in three years. Where the trend is clear, it is usually cheaper to leave space in the civil works than to retrofit later.
Does the coagulant choice affect compliance?
Yes, in two ways that are easy to miss. Chloride-based coagulants such as ferric chloride add chloride to the effluent, which matters where a chloride or conductivity limit applies or where water is reused for irrigation. And acidic coagulants consume alkalinity, which can push treated pH below the lower bound of the consent — a compliance failure caused by the chemical rather than the process. See the chemicals selection tables.
How often is this page updated?
Countries are added as each instrument is verified. Published country data is rechecked annually against the current text of the law, and each entry carries the date of its last check. Environmental legislation changes, and a table without a date on it is worthless.