Tannery DAF pilot: measured performance

This case records pilot tests on real tannery wastewater after screening, homogenisation and sulphide oxidation. Location and operator identity are deliberately withheld; the test conditions and measured water-quality data are retained because they are unusually detailed for tannery flotation.

Case outcome

At an influent flow of 2.0–2.9 m³/h with 50–100% treated-water recycle, dissolved air flotation reduced suspended solids from 2,680 to 640 mg/L and COD from 2,110 to 1,150 mg/L. The measured reductions were 76.1% TSS and 56.5% COD.

1.8 m²Flotation area
1.2 m³Flotation volume
2.0–2.9 m³/hRaw influent
76.1%TSS reduction
56.5%COD reduction

DAF configuration and operating window

The pilot DAF had a 1.8 m² net flotation zone and approximately 1.2 m³ flotation volume. It used a pressurisation tank, pressure-release zone, treated-effluent recycle tank and a variable-speed mechanical scraper for both floated and bottom solids.

Operating itemRecycle testDirect-pressurisation comparison
Raw influent flow2.0–2.9 m³/h3.6 m³/h
Recycle ratio50–100%None
Total flow through cell3.8–4.1 m³/h3.6 m³/h
Pressure5 bar2.5–3.0 bar
Air flow0.30–0.45 Nm³/h0.05–0.10 Nm³/h
Surface hydraulic loading1.1–1.6 m³/m²·h2.0 m³/m²·h
Flotation detention time25–30 min20 min
The recycle test is the basis for the measured water-quality result below. The direct-pressurisation run was a comparison mode, not a separate full performance claim.

Measured influent and DAF effluent

ParameterInfluent after equalisationDAF effluentMeasured reduction
Settleable solids102 mL/L0.4 mL/L99.6%
Suspended solids2,680 mg/L640 mg/L76.1%
COD2,110 mg/L1,150 mg/L56.5%

Chemistry and operation lessons

The best efficiency/cost balance in the recycle test was reported near 400 mg/L alum, without polyelectrolyte. In the direct-pressurisation test, the reported chemical programme was 300 mg/L alum plus 0.5 mg/L polyelectrolyte.

The important operational lesson is that more air was not automatically better. Excessive air flow created turbulence and destabilised the float layer, causing some sludge to settle. The tests found that raw tannery wastewater could be pressurised directly, but chemical addition after pressurisation and careful scraper speed were important to avoid shearing the floc.

How to use this case in real design

This was a pilot, not a plant capacity guarantee. It is valuable because it reports the hydraulic conditions, pressure, recycle, air-to-solids range and laboratory results on actual tannery wastewater. For design, treat the reported 1.1–1.6 m³/m²·h as a conservative pilot reference and validate the chemical dose, air-to-solids ratio and float stability with a jar test and a pilot where raw wastewater varies significantly.

Evidence and limits

This page is based on an independent public tannery-treatment pilot report. The operating setting and participant details have been redacted on this website. Numbers shown are reported measured results from the stated test conditions. They demonstrate process capability; they are not a performance warranty for another tannery or an unsegregated wastewater stream.