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SWRO Pre-Treatment DAF

Seawater DAF system reducing TEP and AOM loading ahead of SWRO membranes, extending CIP intervals from 30 to 72 days at a 45 MLD desalination plant.

Client Overview

A 45 million litres per day (MLD) seawater reverse osmosis (SWRO) desalination plant on the Mediterranean coast. The facility supplies potable water to a coastal city of 180,000 residents and adjacent agricultural irrigation networks. The plant had operated since 2012 with conventional dissolved air flotation (DAF) pre-treatment, but membrane fouling had progressively worsened.

"Membrane fouling was our biggest operational headache. CIP frequency had doubled in three years, and we were consuming chemicals faster than our original design basis. The DAF retrofit completely changed our operating feasibility."

— Plant Manager, Mediterranean SWRO Facility

The Challenge

The plant's original DAF system was engineered for conventional seawater with low organic loading. However, seasonal harmful algal blooms (HABs) and increasing transparent exopolymer particle (TEP) concentrations had created a fouling crisis:

  • Membrane CIP frequency: Every 30 days (design: 60 days) — consuming 12,000 L chemicals/month
  • Pressure drop increase: Normalised differential pressure rising 0.15 bar/week during bloom events
  • TEP breakthrough: DAF effluent TEP > 400 µg/L Xanthan eq. (target < 150 µg/L)
  • AOM spikes: Biopolymer concentrations peaking at 2,800 µg/L during summer HABs
  • Filter run times: Dual-media filters blinding in 8-12 hours (design: 24 hours)

The Solution

Reynolds & Bauhm proposed and was involved in delivering a two-phase upgrade combining hydraulic optimisation and coagulation chemistry improvement.

Phase 1: CFD-Optimised DAF Contact Zone

Reynolds & Bauhm engineers modelled the existing DAF using ANSYS Fluent with multiphase flow (water + air bubbles). The simulation identified:

  • Bubble size distribution skewed toward >100 µm bubbles (optimal: 30-60 µm)
  • Contact time of only 2.1 minutes (required: >4 minutes for TEP floc)
  • Short-circuiting via an unbaffled outlet weir

Reynolds & Bauhm proposed and supervised the design and installation of:

  • Revised saturator system: Pall ring-packed saturator with pressure control to 5.5 bar, achieving 70-80 micron bubble Sauter mean diameter
  • Extended contact zone: Baffle extension increasing effective retention to 5.2 minutes
  • Variable-speed recycle pump: Automated flow pacing from 8-15% of forward flow based on raw water turbidity

Phase 2: Coagulation Optimisation

Jar testing with site seawater identified that ferric chloride at 3.5 mg/L as Fe achieved superior TEP removal versus the existing alum dose of 8 mg/L as Al:

  • TEP removal improved from 45% to 78%
  • Lower sludge volume (ferric hydroxide denser than alum floc)
  • Better performance across pH 7.8-8.3 (seawater natural range)
DAF Flotation Unit (Retrofit)
Packed Saturator (Pall Rings)
Ferric Chloride Dosing System
SCADA with Turbidity Feedback

Results

Before

  • CIP interval: 30 days
  • TEP in DAF effluent: 420 µg/L
  • Filter run time: 8-12 hours
  • Membrane DP rate: +0.15 bar/week

After

  • CIP interval: 72 days
  • TEP in DAF effluent: 135 µg/L
  • Filter run time: 26-30 hours
  • Membrane DP rate: +0.04 bar/week

Operational & Financial Impact

ParameterBeforeAfterAnnual Reduction
CIP chemical consumption (acid, caustic, bisulphite)12,000 L/mo4,800 L/mo
Membrane replacement rate8.5%/yr3.2%/yr
Filter backwash water4.2% of feed1.8% of feed
Power (CIP pumps, heaters)185 MWh/yr72 MWh/yr
Operator overtime (CIP events)340 hrs/yr140 hrs/yr
Total annual Operating expenditure reduction

Compliance & Standards

The upgraded pre-Treatment Process maintains full compliance with WHO Guidelines for Drinking Water Quality and EU Drinking Water Directive (2020/2184). Post-DAF silt density index (SDI) consistently measures 2.8-3.4 (target < 4.0), and modified fouling index (MFI-0.45) is maintained below 3 s/L².

Key Learning

TEP and AOM removal in seawater DAF is fundamentally a contact-time and bubble-size challenge, not merely a chemical dosing problem. Conventional DAF designs optimised for suspended solids removal often fail with transparent, neutrally-buoyant biopolymers. CFD-guided hydraulic modification combined with ferric-based coagulation provides a robust, lower-Operating expenditure alternative to granular activated carbon or ultrafiltration pre-treatment.

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Protect Your SWRO Membranes

DAF pre-treatment systems engineered for TEP and AOM removal, with CFD validation and pilot testing for seawater applications.

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