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Coagulants

Inorganic and organic coagulants for destabilising suspended colloids in raw water, effluent treatment, and industrial process water, enabling efficient downstream clarification and sedimentation.

Raw Water Treatment Wastewater Treatment PAC Ferric Salts
Primary Chemistry
PAC · Ferric Chloride · Ferric Sulfate · Alum
Mechanism
Charge Neutralisation & Sweep Flocculation
Effective pH Range
4.5 – 8.5 (product-dependent)
Forms Available
Liquid · Powder · Granular

Overview

Coagulants are chemicals that destabilise the colloidal and fine suspended particles naturally present in raw water and industrial wastewater. Colloidal particles (clay, silt, humic substances, biological material) carry negative surface charges that keep them in stable suspension; gravity and conventional filtration cannot remove them efficiently without chemical pre-treatment. Coagulants neutralise these surface charges, allowing particles to aggregate into settleable floc.

In water treatment practice, coagulation is almost always the first chemical step in a treatment train. It directly determines the efficiency of every downstream process, sedimentation, dissolved air flotation (DAF), and filtration. Its correct selection and dosing has an outsized impact on total treatment cost and treated water quality.

Coagulation vs. flocculation: These terms are often used interchangeably but describe distinct steps. Coagulation is the rapid chemical destabilisation of colloids, typically achieved in seconds at high mixing intensity. Flocculation is the slower physical aggregation of destabilised particles into larger, settleable floc, requiring gentle, prolonged mixing. Both steps are required for effective clarification; coagulant selection affects both.

Coagulant Types

Polyaluminium Chloride (PAC)
Pre-hydrolysed aluminium coagulant. More effective than alum at equivalent aluminium dose, produces less sludge, and operates over a wider pH range. Available in powder (28–30% Al₂O₃) and liquid (10–18% Al₂O₃). The preferred coagulant for most modern WTPs. See the dedicated PAC page for detailed specifications.
Alum (Aluminium Sulfate)
Traditional inorganic coagulant in widespread use. Lower cost per tonne than PAC but requires higher dosing and produces more sludge. pH must be maintained above ~6.0 for effective coagulation; poorly buffered source waters may require lime or soda ash addition. Available in lump, granular, and liquid forms.
Ferric Chloride (FeCl₃)
Strong inorganic coagulant with an effective pH range of 4.0–7.5. Superior to aluminium coagulants for phosphorus precipitation and for highly coloured (humic-rich) source waters. Dense, fast-settling floc. Corrosive in liquid form, requires appropriate dosing and storage infrastructure. Widely used in industrial and municipal wastewater treatment.
Ferric Sulfate (Fe₂(SO₄)₃)
Similar performance to ferric chloride but without the chloride loading, preferred where chloride content in treated water or effluent must be minimised. Effective for phosphorus removal and colour treatment. Available in granular and liquid forms.

Applications

Application Treatment Objective Recommended Coagulant
Municipal raw water treatment Turbidity and colour removal from river and reservoir intakes ahead of sedimentation and filtration PAC (liquid or powder); ferric chloride for highly coloured water
Industrial effluent treatment Suspended solids removal, phosphorus precipitation, and COD reduction before biological treatment or discharge Ferric chloride or ferric sulfate for phosphorus-heavy streams; PAC for general clarification
Cooling water makeup pre-treatment Removal of suspended solids that foul heat exchanger surfaces and promote under-deposit corrosion in cooling towers PAC at low-to-moderate dose; jar test required to establish optimum for local source water
Boiler feedwater pre-treatment Clarification of raw water before softening and demineralisation to protect ion exchange resins and membranes PAC; compatibility with downstream treatment must be verified to avoid aluminium carryover to boiler
Petrochemical & refinery WTP Clarification of river or seawater intake; treatment of oily wastewater and process water before reuse or discharge PAC for intake; ferric salts for oily/phosphorus-laden wastewater; dose optimisation by jar test on actual stream
LNG plant, seawater intake Turbidity and biofouling precursor removal from seawater before desalination or cooling water distribution PAC or ferric sulfate; chloride tolerance of downstream membranes governs coagulant selection

Petrochemical & LNG Applications

Oil & gas, petrochemical, and LNG facilities operate large-volume water systems, such as cooling towers, boilers, firewater systems, and wastewater treatment plants, that require the same coagulation chemistry used in municipal WTPs, but with additional constraints driven by the process environment.

In refineries and petrochemical plants, coagulants are used in the intake water treatment system to prepare river or groundwater for use as cooling water makeup and boiler feedwater. Refinery effluent treatment plants (ETPs) typically use ferric coagulants for the removal of emulsified hydrocarbons, suspended solids, and phosphorus from process drains before biological treatment and final discharge. Correct coagulant selection is critical to meeting PROPER and local AMDAL discharge standards.

In LNG terminals, seawater is used as a heat transfer medium in the liquefaction process and in Open Rack Vaporisers (ORVs). Coagulants are applied at the seawater intake to remove suspended matter and reduce biofouling precursor load before the water enters the cooling system. Where desalination provides process and potable water, coagulation is the primary pre-treatment step protecting downstream RO membranes from fouling.

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