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Lamella clarifiers

A lamella clarifier is a mechanical separation stage in which suspended solids denser than water settle onto inclined plates and slide down them into a hopper. The plate pack provides a settling area many times greater than the floor area the unit stands on, so the same duty is performed in substantially less space than a horizontal settling tank requires.

  1. Screens and balancing
  2. Reagent dosing
  3. Lamella clarifiers
  4. Biological treatment
  5. Sludge dewatering
  6. Effluent polishing

Principle

How it works

The unit is a vessel with a conical hopper at the bottom and a pack of inclined plates in its middle section. Effluent enters beneath the pack, rises through the channels between the plates, and the clarified water is collected by overflow launders at the top, while the settled matter travels down the plates against the flow and accumulates in the hopper. There are no moving parts inside the vessel: separation is driven by gravity.

Removal is governed not by residence time but by the ratio of two quantities: the settling velocity of the particle — its hydraulic size — and the hydraulic loading, that is, the flow divided by the settling area. A particle is removed if it reaches the surface of a plate before the flow carries it out of the channel. The settling velocity itself follows Stokes' law: it is proportional to the square of the particle size and to the density difference between particle and water, and inversely proportional to the viscosity of the water.

The plate pack increases not the length of the water's path but the number of settling surfaces. Between adjacent plates a particle has to travel not the full depth of the vessel but a distance of a few centimetres, and the time it needs to reach a surface is shortened in the same proportion. The total projected area of the pack — the sum of the horizontal projections of all the plates — is several times the floor area the unit occupies; the exact ratio depends on the number of plates, their size and the angle of inclination.

Flow within the channels has to remain laminar: any mixing returns a settled particle to the flow. Hence the requirement that the flow be distributed evenly among all the channels of the pack: where some channels are overloaded and others underloaded, the area actually working is smaller than the design value.

The angle of the plates is chosen so that sludge slides down continuously rather than accumulating: it is normally 55–60° to the horizontal. The sludge slides into the hopper, thickens there and is withdrawn by pump, either on a timer or by level. Fine and colloidal solids are enlarged with reagents ahead of the clarifier: a coagulant neutralises the charge of the colloidal particles and a flocculant binds the microflocs into structures whose settling velocity suffices for the design regime.

Principle

The counterintuitive part

Inclined plates work not by lengthening the path of the water but by shortening the height a particle has to travel to a settling surface. In a horizontal tank that is metres; in a plate pack it is centimetres between adjacent surfaces. The consequence runs against the usual expectation: increasing the volume of the unit achieves nothing in itself, whereas increasing the settling area has a directly proportional effect. That is why a lamella clarifier of a given capacity occupies several times less space than a horizontal tank, and why sizing it by residence time is pointless.

Sludge has to slide down off the plates continuously, and for that reason the angle of inclination and the properties of the sludge are bound together. Sticky, fibrous or poorly thickening sludge is retained between the plates, part of the channels drops out of service, and the unit loses settling area while remaining formally in order: the flow passes, there are no moving parts, there is nothing to fail. This shows only as a rise in suspended solids at the outlet, which is why a sample after the clarifier is not a reporting formality but the one direct indication of the state of the pack.

The same unit removes less in winter than in summer, and the equipment is not the reason. Settling velocity is inversely proportional to the viscosity of water, and the viscosity at 5 °C is roughly 1.7 times that at 25 °C. The settling velocity of the same particles falls in the same proportion, and part of the solids that reported to the sludge in warm weather passes straight through. Sizing on summer samples for an unheated site leads to exceedances in precisely the cold season.

Practice

What that gives in practice

The principal practical gain is the space occupied. A lamella clarifier fits where a horizontal tank does not fit at all: in the refurbishment of existing treatment works, inside an existing building, on a confined site. That is usually what decides the choice, since the separation principle of the two is the same.

In an effluent treatment scheme the stage sits after reagent treatment and ahead of polishing or biological treatment. It removes the bulk of the suspended solids and the share of COD bound to them; parameters relating to dissolved matter stay as they were, and where the exceedance concerns those, settling alone does not resolve it.

On mineral solids the stage works without reagents at all — this is the case in which operation costs least: what remains is the power for sludge withdrawal and the handling of the sludge itself. On colloidal and hydroxide solids a reagent side is mandatory, and maintaining it becomes the principal operating cost.

The achievable reduction is assessed from comparable samples at inlet and outlet, not from the appearance of the clarified water. On heavy mineral solids at the design hydraulic loading it is usually 70–90 % for suspended solids and can be higher on flocs produced by a matched reagent regime; on fine solids without coagulation the result may be close to zero with the unit entirely in order.

The unit is assembled from a vessel, a plate pack, the clarified water collection arrangement and a sludge hopper, and is supplied for a particular flow and connection. We do not manufacture it: our part of the work is the effluent analysis and the settling test, the determination of hydraulic size and of the settling area required, the selection of size and ancillaries, supply, commissioning and subsequent service.

Limits

When you need it

  • Mineral solids predominate in the effluent: machining of metal and stone, aggregate washing, concrete production, quarry and wash waters.
  • Reagent treatment is already in operation at the plant — neutralisation or metal precipitation — and the hydroxide sludge produced has to be separated from the water.
  • Space is limited: a horizontal tank of the area required does not fit on the site, and the works are being rebuilt within their existing footprint.
  • Suspended solids have to be brought within the municipal sewer discharge limits or within the requirements of the next stage.
  • The stage is needed as pre-treatment ahead of filtration, sorption or membrane separation, for which suspended matter is the main cause of premature failure.
  • Stormwater and surface runoff from industrial sites, where the main load is sand and mineral solids.

When it will not help

  • Where the main load is fats, oils and petroleum products. Being lighter than water, they do not settle; dissolved air flotation is designed for them, a particle being lifted by an air bubble attached to it.
  • Where the exceedance concerns dissolved matter — salts, ammonium nitrogen, dissolved organics. Settling has no effect on them; biological treatment, sorption or membrane processes are required.
  • Where the solids are fine and stable and no reagent side can be organised on the site. Without coagulation the settling velocity of such solids is close to zero, and a larger unit will not change it.
  • Where the sludge is sticky or fibrous: wool, natural and synthetic fibre, waterlogged fatty organics. Sludge of that kind does not slide but fastens between the plates, and the pack has to be withdrawn and washed by hand.
  • Where the flow is extremely uneven and no balancing tank is provided. On a brief excursion above the design hydraulic loading the flow carries already settled matter out of the channels, and the suspended solids at the outlet may at that moment exceed those at the inlet.

Practice

Typical cases

Feed
Electroplating shop effluent after the neutralisation unit: suspended solids around 400 mg/l as metal hydroxide flocs, pH corrected to 8.5–9, flow 8 m³/h over two shifts.
Task
Separate the hydroxide flocs from the water and meet the discharge limits for suspended solids and metals.
Scheme
Balancing tank → neutralisation → flocculation chamber → lamella clarifier → pressure filter → outfall; sludge from the hopper to dewatering.
Result
The metals leave with the sludge, since in insoluble form they belong to the suspended fraction. A filter downstream of the clarifier is needed because part of the finer flocs settle more slowly than the design value and pass through the pack. The sludge is a hydroxide sludge, releases water poorly and calls for dewatering equipment rather than storage in a tank.
Feed
Recycled water from a stone sawing area: mineral solids up to 3000 mg/l, predominantly coarse particles, flow 15 m³/h, shop temperature, steady.
Task
Clarify the water to a state fit for return to the saws without setting up a reagent side in the shop.
Scheme
Sump with grit trap → pump → lamella clarifier → recycled water tank; sludge to dewatering.
Result
The solids are mineral and heavy, so the scheme works without a coagulant. The governing quantity turns out to be not the inlet concentration but the mass of sludge produced: at 3000 mg/l and 15 m³/h some 45 kg of dry solids an hour leave the water, and the hopper volume and withdrawal regime are planned for that mass.
Feed
Surface runoff from a bulk materials storage yard: sand and mineral solids, a surge after rainfall, design flow 20 m³/h, petroleum products low in content but subject to a limit.
Task
Bring the runoff within the discharge limit for suspended solids without exceeding the limit for petroleum products.
Scheme
Grit trap → attenuation tank → lamella clarifier → sorption unit → outfall.
Result
The clarifier removes sand and mineral solids. It does not remove petroleum products: they are lighter than water, and their limit is met by a separate stage. The attenuation tank is mandatory — without it the design hydraulic loading is exceeded within the first minutes of rainfall.

The cases are typical examples, not site reports.

Innovations

Our developments for this stage

Scheme

Place in the scheme

A lamella clarifier hardly ever works on its own. Ahead of it a screen or sieve and a grit trap are needed: coarse matter enters the channels of the pack and lodges between the plates, while abrasive sand wears them. A balancing tank evens out the flow and with it the hydraulic loading, on which removal directly depends.

Where the solids are fine, colloidal or hydroxide, a dosing station and a flocculation chamber are placed ahead of the clarifier. What matters is not only the dosing itself but the stretch between the chamber and the unit: flocs already formed are broken up by a pump, by an abrupt reduction in section and by a long pressure line, and what reaches the plates is matter that no longer settles. The flocculation chamber is therefore placed immediately adjacent and the effluent brought in by gravity where the hydraulic levels allow.

Downstream of the clarifier the scheme divides. Clarified water goes to biological treatment, to polishing by filtration or to discharge, depending on which parameters remain out of limits. Sludge from the hopper goes to dewatering: hauling it at high moisture is not economically justified, and its volume is set by the mass of solids removed rather than by the size of the unit.

Hydraulic levels are fixed at the scheme stage, not during installation. The unit works by gravity if the difference between inlet and outlet levels covers the head loss in the pack and the launders; otherwise a pump is added to the scheme, and with it the breaking up of flocs.

Scheme

Automation and control

  • A lamella clarifier has little control of its own: there are no moving parts inside the vessel and nothing within the unit to regulate. The regime is set by the stages before and after it, so automation here belongs to the scheme as a whole rather than to the equipment of the stage.
  • Reagent dosing proportional to effluent flow and, where the composition demands it, corrected by pH. A fixed dose at variable flow means either excess reagent consumption or a failure of settling at peak load.
  • Sludge withdrawal from the hopper on a timer or by a sludge level sensor. Infrequent withdrawal lets the sludge level reach the lower edge of the pack, and carry-over of solids begins with the flow readings unchanged; frequent withdrawal draws off mostly water and increases the volume sent to dewatering.
  • Monitoring of clarified water turbidity and recording of flow. The turbidity reading at the outlet is the one direct and continuous indication that the plate pack is working; the flow is needed both for dosing and to distinguish a blinded pack from an excursion above the design hydraulic loading.

Operation

Running it

Energy

The stage has virtually no energy consumption of its own: separation is driven by gravity, and where the difference in hydraulic levels is sufficient the effluent passes through the unit by gravity too. Power is consumed by the ancillaries — the feed pump where gravity flow is impossible, the sludge pump, the flocculation chamber stirrer and the dosing station. With gravity feed and intermittent sludge withdrawal the total specific consumption stays within hundredths of a kilowatt-hour per cubic metre of effluent, appreciably below that of dissolved air flotation of the same capacity. Where the effluent has to be pumped, the governing item is not the stage itself but the head that has to be generated.

Consumables

  • Coagulant — only in schemes with fine, colloidal or hydroxide solids; the dose is established by settling tests and revised when production changes
  • Flocculant — wherever the coagulant is used: it requires solution make-up, accurate concentration control and dosing into the flocculation chamber rather than into a pipe
  • Neutralisation and pH correction chemicals where metals are precipitated as hydroxides: the range of minimum solubility differs for each metal, and staying within it decides the result
  • Wash water and labour for periodic cleaning of the plate pack, and replacement of individual sections and seals where they are damaged
  • Laboratory analyses of suspended solids at inlet and outlet: they are both the basis for tuning the regime and the record submitted to the regulator

What goes to drain

What leaves the water is sludge — the whole mass of retained solids together with reagent flocs where reagents have been used. Its quantity follows from the mass of suspended solids removed, not from the size of the unit: at a concentration of 500 mg/l and a flow of 10 m³/h some 5 kg of dry solids an hour leave the water. The moisture of the withdrawn sludge depends on its nature and on how often it is withdrawn: mineral sludge thickens in the hopper appreciably better than hydroxide sludge, which holds water and almost always calls for dewatering on a screw or belt press. The hazard class and the permitted route are determined by the composition of the sludge rather than by the type of equipment.

Sizing

Sizing

What we account for

  • The hydraulic size of the solids — the settling velocity of the particles, determined by a settling test in a cylinder: the fraction settled after 30, 60 and 120 minutes, not a single concentration figure
  • The nature of the solids: mineral, hydroxide, organic, fibrous — it governs both the applicability of the stage and the tendency of the sludge to be retained between the plates
  • Flow: average and maximum hourly, daily variation, the nature of surges
  • Inlet suspended solids and the value required at the outlet: their difference sets the mass of sludge, the hopper volume and the withdrawal regime
  • The reagent regime where one is required: type and dose of coagulant and flocculant, the need for pH correction, the position of the flocculation chamber
  • Effluent temperature: it governs the viscosity of the water and hence the settling velocity, and the calculation is made for the least favourable season
  • Site characteristics: the footprint and height of the unit, the hydraulic levels of inlet and outlet, the route for sludge and access for withdrawing the plate pack

What a wrong choice costs

  • Sizing on volume or on residence time. The governing quantity is the settling area, not the volume: a unit of the right volume with insufficient area removes only the coarse fraction, and that shows up in the very first analyses.
  • Sizing on flow with no settling test. On their data sheets units of the same capacity are identical, yet on different effluents they give different results, because the hydraulic size of the solids differs.
  • Applying the stage to effluent carrying fats and petroleum products. The floating fraction does not settle, collects under the upper edges of the plates and leaves with the clarified water, and as it builds up it also hinders the sliding of the sludge.
  • No flocculation chamber where the solids are colloidal, or a chamber placed behind a pump and a long pipeline. In the first case flocs do not form, in the second they form and are broken up before reaching the plates; the outcome is the same either way.
  • No provision for sludge withdrawal and dewatering. The hopper fills, the sludge level reaches the lower edge of the pack, and carry-over of solids begins with the unit entirely in order and the flow readings unchanged.
  • Calculating from summer samples for an unheated site. In winter the viscosity of the water is higher and the settling velocity lower, and the limit is breached in precisely the season the calculation was not made for.

Sizing

What we need for a calculation

  • An effluent analysis report: suspended solids, COD, pH, temperature, and also fats and petroleum products — they decide whether settling applies at all
  • The result of a settling test in a cylinder, or the possibility of running one: the fraction settled after 30, 60 and 120 minutes
  • The origin of the solids: which process produces them and what they are by nature — mineral, hydroxide, organic, fibrous
  • Flow: average and maximum hourly, the production schedule, the nature and frequency of surges
  • Requirements at the outlet: discharge limits or the requirements of the next treatment stage
  • The existing scheme: screens, grit traps, balancing tank, dosing station, structures already in operation
  • Site characteristics: free floor area and ceiling height, the hydraulic levels of the effluent inlet and the clarified water outlet, where the sludge is routed, access for servicing the plate pack

Questions

Questions

How does a lamella clarifier differ from an ordinary horizontal tank?

The separation principle is the same: both settle whatever is heavier than water. The difference lies in where the settling surface is. A horizontal tank has one — the floor — and its area equals the area of the structure. A lamella clarifier has as many surfaces as there are plates. Hence at equal capacity the lamella unit occupies several times less space, and it is that, rather than the quality of clarification, which usually decides the choice.

Does a clarifier need reagents?

It depends on the nature of the solids. Mineral solids — sand, machining particles — settle without reagents, and the scheme is then the simplest to operate. Fine and colloidal solids have a settling velocity close to zero and pass through the unit whatever its size unless a coagulant and a flocculant are used. Metal hydroxides are by definition formed by reagents, so there a reagent side exists in any case. What a particular effluent requires is shown by a settling test, not by the industry it comes from.

Lamella clarifier or flotation unit?

A clarifier settles what is heavier than water: mineral solids, sand, hydroxide flocs formed by reagent treatment. A flotation unit lifts what is lighter than water or can be made lighter by attaching an air bubble to the particle: fats, oils, petroleum products, light organics, surplus activated sludge. All they share is the reagent preparation ahead of the unit. Where the effluent carries both, the stages are applied in sequence rather than chosen between.

Why is there no price in the catalogue?

A lamella clarifier is engineered equipment. The settling area, the number and material of the plates, the hopper volume and the make-up of the dosing and sludge withdrawal arrangements follow from a calculation for the particular effluent, not from the flow alone: two units rated at 10 m³/h may differ both in pack area and in ancillaries. The models in the catalogue therefore read "on request", and a price is quoted once the effluent composition and the outlet requirements are known.

What happens if sludge is retained between the plates?

The working settling area shrinks and suspended solids begin to pass to the outlet. The unit meanwhile remains formally in order, and there is one indication — a rise in turbidity and in suspended solids in the clarified water. The remedy depends on the cause: a change in the frequency of sludge withdrawal, an adjustment of the reagent regime or, where blinding persists, withdrawal of the pack sections and washing. Sludges liable to blind the pack are better identified before ordering, during the settling test.

Can a unit be taken with a margin on area?

A margin on settling area acts directly: it lowers the hydraulic loading and raises the share of solids removed, and there is practically no lower bound on flow of the kind dissolved air flotation has. A margin does not, however, replace reagent preparation: particles whose settling velocity is close to zero are not removed at any area.

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