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DAF–UF Pre-Treatment: Operational Resilience Through a Seasonal Raw-Water Collapse

A 2,500–10,000 m³/hr dissolved-air-flotation (DAF) and ultrafiltration (UF) pre-treatment facility lost stability when wet-season raw-water turbidity rose over 250 %. Using 275 logged operational records, we traced the cascade to three interdependent failures — and set out the fixes that restore resilience without major capital spend.

The Headline Numbers

2,500–10,000 m³/h

Treatment capacity across six parallel DAF streams.

+250 %

Rise in intake turbidity entering the wet season (3.5 → 12.3 NTU mean, peak 146 NTU).

275

Logged operational entries analysed across dry and wet seasons.

3 root causes

Interdependent failures in saturator pressure, dosing and flocculation.

Anonymised from a six-month commissioning and early-operation dataset. Figures are the client’s logged operating data.

A Stable Plant Met an Unstable Source

DAF followed by UF is a proven pre-treatment configuration for surface and reclaimed water — but the integrated process is sensitive to rapid swings in turbidity, organic loading and hydraulic shock. This facility treated a variable open surface-water source through six parallel DAF streams (ferric-chloride coagulation, acid pH correction, anionic-polymer flocculation) ahead of UF membranes. The transition from a calm dry season to a highly variable wet season was abrupt: mean intake turbidity tripled from 3.5 to 12.3 NTU, with isolated peaks above 140 NTU, while algae and organic loading rose — lifting coagulant demand and straining flocculation kinetics just as flows climbed toward 10,400 m³/hr.

As Configured

Intake

Open surface-water source with seasonal turbidity excursions.

Coagulation

Ferric chloride (FeCl₃) dosing, target 2.5–4.0 mg/L as Fe.

pH Correction

Acid dosing to hold coagulation pH, typically 6.4–7.2.

Flocculation

Two-stage mechanical flocculation, variable-speed mixers (0–70 %).

Flotation

Six parallel DAF streams — independent saturators, recycle pumps and scrapers.

Filtration

UF feed tank receiving the combined DAF clarified water.

DAF Performance Varied Sharply Between Streams

Streams 1 and 3 stayed consistent; Streams 2, 4 and 5 repeatedly exceeded 20 NTU. During several high-turbidity events outlet turbidity exceeded intake — negative removal, from sludge carryover, poor bubble–floc attachment or inadequate air dissolution.

DAF StreamMean Outlet Turbidity (NTU)Peak Outlet Turbidity (NTU)
Stream 15.427.1
Stream 211.625.2
Stream 36.821.7
Stream 411.925.9
Stream 57.433.6
Stream 69.011.7

Saturator Pressure Collapses

Target 4.2–5.5 bar, but logs recorded repeated drops to 1.5–3.0 bar — one recycle-pump fault ran ~10 h overnight. Open air-release valves and saturator blockages also featured.

Chemical-Dosing Reliability

A compressor failure stopped all coagulant and acid dosing until manually corrected; a closed ferric valve went undetected; acid-valve feedback faults caused intermittent over- and under-dosing.

Flocculation & Scrapers

Mixer trips during electrical storms lost first-stage flocculation on three streams; timed-scraper operation to save power caused sludge-hopper overflow under high solids.

UF Feed Quality Degraded Substantially

DAF instability passed straight through to the membranes — raising fouling risk and threatening permeability.

ParameterPeriod A Mean (dry)Period B Mean (wet)Peak Recorded
UF Turbidity4.4 NTU10.5 NTU36.6 NTU
UF TSS3–8 mg/L5–37 mg/L37 mg/L
UF Feed pH6.867.208.00

On-site jar tests during wet-season operation gave floated-sludge TSS from 4 to 64 mg/L across identical intervals — inconsistent floc structure or bubble distribution even when upstream chemistry looked stable. pH tracked well at 6.8–7.2 but scattered badly above 7.5, pointing to acid-dosing capacity / mixing limits and sensor drift.

62 Logged Events, by Type

CategoryShare
Equipment faults / trips18 %
pH & control issues18 %
Chemical-dosing adjustments18 %
Sludge & scraper problems10 %
Weather-related events8 %
Pressure & flow anomalies6 %
Calibration & maintenance6 %

Operational Overview — the Six-Month Record

The full operational dataset behind the findings, panel by panel.

Intake Flow vs Turbidity

Intake Flow vs Turbidity

Intake flow (blue) against turbidity (red, right axis). The sharp wet-season turbidity spikes — peaks above 140 NTU — against rising flow show the abrupt source deterioration the plant had to absorb.

Chemical Dosing Trends

Chemical Dosing Trends

Ferric, acid and polymer dosing over the period. Ferric was escalated through the wet season; acid dosing is intermittent, reflecting the valve and feedback faults that repeatedly disrupted coagulation.

pH Profile Through Treatment

pH Profile Through Treatment

Intake, dosed and UF-feed pH. They track well during stable periods but diverge during upsets — evidence of acid-dosing capacity / mixing limits and pH-sensor drift.

DAF Outlet Turbidity by Stream

DAF Outlet Turbidity by Stream

Outlet-turbidity distribution per DAF stream. Streams 1 and 3 stay tight and low; Streams 2, 4 and 5 spread high with frequent outliers above 20 NTU.

UF Feed Quality Parameters

UF Feed Quality Parameters

Turbidity, TSS and iron reaching the membranes. The wet-season excursions (turbidity to 36.6 NTU) map directly onto the upstream DAF instability.

DAF Saturator Pressure Trends

DAF Saturator Pressure Trends

Saturation pressure per stream. Repeated collapses from the 4.2–5.5 bar target down to 1.5–3.0 bar coincide with the poor-performing streams — the primary constraint on flotation.

Intake Algae vs UF Turbidity

Intake Algae vs UF Turbidity

Intake algae against UF turbidity. Elevated-algae periods cluster with higher UF turbidity, linking bloom loading to membrane-feed quality.

Operational Events by Month

Operational Events by Month

Logged operator comments per month, peaking in the wet-season months — a proxy for operational stress and intervention frequency.

DAF Performance & Efficiency

Per-stream performance, dosing efficiency and control accuracy.

DAF Turbidity Removal Efficiency

DAF Turbidity Removal Efficiency

Removal efficiency by stream. Negative values (outlet worse than intake) are common on Streams 2, 4 and 5 — confirming sludge carryover and poor bubble–floc attachment; Streams 1 and 3 hold the highest median.

Ferric Dose vs UF Residual Fe

Ferric Dose vs UF Residual Fe

Ferric dose against residual iron in the UF feed. Higher dosing does not reliably raise residual iron, pointing to variable coagulation efficiency or ferric-hydroxide precipitation.

pH Control: Dosed vs Actual

pH Control: Dosed vs Actual

Dosed setpoint vs actual UF-feed pH against the 1:1 line. Points below the line indicate acid underdosing or mixing delay; the scatter above 7.5 shows control breaking down at high demand.

DAF Operational Status Mentions

DAF Operational Status Mentions

Online / offline / fault mentions per stream from the logs. Streams 2, 4 and 5 carry the most offline and fault mentions — consistent with their poorer turbidity removal.

Three Interdependent Failures

The critical vulnerability was not the peak turbidity itself — it was the interdependence of three systems. When one failed, the others could not compensate.

1 · Saturator Pressure

The primary constraint. Low pressure cuts air-dissolution efficiency, producing larger bubbles and weaker floc–bubble agglomerates — directly raising outlet turbidity and sludge carryover.

2 · Dosing Vulnerability

A single air supply for dosing-valve actuation was a single point of failure; valve-position feedback faults broke closed-loop control of coagulant and acid.

3 · No Wet-Season Protocol

No pre-emptive plan existed to raise coagulant, cut flow or switch scrapers to continuous before raw-water turbidity peaked.

Restoring Resilience — Without Major Capital

Saturator Redundancy

Pressure monitoring with automatic alarms and standby-compressor switching to prevent pressure collapse; auto-reduce stream flow or take a stream offline below 3.5 bar.

Dosing-Valve Redundancy

Redundant air supply to dosing actuators with verified fail-safe positions, ending the single-point-of-failure on coagulant and acid delivery.

Feed-Forward Coagulation

Link raw-water turbidity to automatic FeCl₃ dose escalation, removing operator lag during storm events.

Scraper Duty Cycle

Automatically switch scrapers to continuous operation when DAF inlet turbidity exceeds a threshold (e.g. 10 NTU) to stop hopper overflow.

pH-Sensor Maintenance

Increase inline pH-sensor calibration frequency — drift was a recurring cause of dosing error.

Storm-Response Protocol

A pre-emptive checklist for forecast heavy rain: FeCl₃ to 4.0 mg/L and polymer to 0.6 mg/L, cut flow 15–20 %, scrapers continuous, raise hopper-pump frequency.

Benchmark the Best Streams

Use Streams 1 and 3 as the baseline; investigate header configuration, orifice sizing and recycle ratio to lift the underperforming streams.

Diagnostics

A full residence-time-distribution tracer study to check for short-circuiting/dead zones, and a sludge-volume index to predict carryover before it reaches the UF.

From Reactive Fault-Finding to Predictive Management

A DAF–UF pre-treatment plant that runs cleanly in the dry season can cascade into failure when the source deteriorates — not because of peak turbidity, but because saturator pressure, dosing reliability and flocculation stability are interdependent. Hardening those three, with automated storm protocols and redundancy, restores resilience without major capital. Detailed operational logging turned reactive fault-finding into predictive process management — and the facility now serves as a reference for exactly that.

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