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Sludge dewatering

Sludge dewatering is the stage at which water is mechanically separated from the sludge produced by the earlier treatment stages. The stage does not treat water: its purpose is to reduce the volume of waste hauled away and to turn a pumpable mass into a material that is loaded into a skip. The separated water returns to the head of the scheme together with whatever is dissolved in it.

  1. DAF flotation
  2. Lamella clarifier
  3. Flocculant dosing
  4. Sludge dewatering
  5. Haulage of the dewatered sludge
  6. Filtrate returned to the head of the scheme

Principle

How it works

Dewatering proceeds in two stages, and both are present in each of the three machines. First the free water separates: the sludge enters the drainage zone and water passes through the filtering surface under gravity. The remaining mass is then subjected to mechanical pressure and part of the capillary moisture is squeezed out. It is the second stage that distinguishes the machines: the way pressure is generated governs both the achievable cake moisture and the duty cycle.

The flocculant is added ahead of the machine and is part of the process rather than an improvement to it. Water is held by the extensive hydrophilic surface of fine particles, and the particles themselves are smaller than the filtering gap or the pores of the cloth. A polyelectrolyte neutralises their charge and binds them into large flocs within which the water becomes able to separate. Without a flocculant sludge is not dewatered less well — it is not dewatered at all: the particles pass the filtering surface along with the water, blind it and leave with the filtrate, and no cake forms.

The screw press. A shaft of decreasing pitch turns inside a cylinder built up from alternating fixed and moving rings. The gap between the rings serves as the filtering slot, and as the shaft turns the moving rings clear it, so wash water is needed only intermittently and in small quantity. The shaft turns at a few revolutions per minute; pressure comes from the reducing volume of the flight and from a back-pressure cone at the outlet. Hence the low installed power: 1.65 kW in the catalogue models at a capacity of the order of 100 kg DS/h.

The belt press. Sludge is spread over a moving belt and passes a gravity zone, where free water drains away; a wedge zone, where pressure builds up gradually; and a pressing zone, where two belts with the sludge between them run over rollers of decreasing diameter, pressure and shear both rising as the diameter falls. The belts are washed continuously with pressurised water, otherwise they blind within a single pass — the wash water flow is stated in the specifications and, for the model with a working belt width of 1000 mm, amounts to 11.2 m³/h. That water goes entirely into the filtrate.

The chamber filter press. Plates faced with filter cloth are closed into a stack, forming chambers between them; a pump feeds sludge into the chambers under pressure, the filtrate passes through the cloth and the solid phase stays inside. When the chambers are full the feed stops, the stack opens and the cake is discharged. The cycle is a batch one and ends with discharge, so the machine does not run unattended; in return it gives the driest cake of the three, since feed pressure is held throughout the cycle and pressing time is not limited by the rate at which sludge passes through. The defining figure of the sub-series is filtration area: for the CFP100 model it is 100 m².

Principle

The counterintuitive part

The capacity of a dewatering machine cannot be stated as a single number, and a volumetric figure in m³/h means nothing on its own: the machine is limited by the mass of dry solids it can separate in an hour, not by the volume of liquid passed through it. Sludge at 1.00 % dry solids holds about 10 kg of dry solids per cubic metre, so 10 m³/h of such sludge is 100 kg DS/h; the same machine on sludge at 5 % DS will take about 2 m³/h, and that will be the same 100 kg DS/h. This is why the screw press specifications place the volumetric figure next to the concentration at which it was obtained, and why the figures of the sub-series are not comparable directly: belt presses are rated by dry solids, chamber presses by filtration area and by throughput in t/h.

A dewatering machine pays for itself in haulage rather than in treatment. Sludge at 99 % moisture is almost entirely water by mass, and the contractor hauling it away is hauling water. Reducing moisture from 99 to 80 % without losing dry solids leaves 20 % dry solids in the cake instead of one, and at a density close to that of water a tonne of the original sludge yields about 50 kg of cake and about 950 kg of filtrate — a twentyfold reduction. In real schemes the reduction is more modest and depends on the starting concentration: sludge already thickened to 5 % DS gives a fourfold reduction at the same cake moisture.

The water separated from the sludge does not leave the scheme. The filtrate returns to the head of the works, and it is not clean water: dissolved nitrogen and phosphorus remain in it, along with part of the COD and, where dosing is out of order, carried-over fine solids as well. An internal loop appears: the return load increases sludge production, and more sludge yields more filtrate. Where the return is not built into the design of the main structures, the analyses show a rising load on the biological stage with no visible change in the incoming effluent — and the cause is looked for in the wrong place.

Practice

What that gives in practice

The stage sits at the end of the scheme but is calculated together with its beginning. Sludge arrives from a flotation unit, a clarifier or the biological treatment structures, and the water separated from it returns to the same place. Dewatering is therefore designed alongside the main structures rather than fitted to structures already built: otherwise those are sized for a load that ignores the return stream.

The flocculant is matched by testing the actual sludge, not by the type of production. Polyelectrolytes differ in the sign and density of their charge and in molecular weight, and sludge of one and the same origin — surplus activated sludge from two neighbouring plants, say — may call for different grades. Choosing by analogy yields either no floc at all or a reagent consumption several times higher than needed.

The choice between the sub-series is governed by the duty of the site as much as by capacity. A screw press runs continuously at low speed, needs little wash water and tolerates swings in concentration — a solution for small and medium flows and for sites without a permanent operator. A belt press is also continuous and takes a larger flow, but requires continuous washing of the belts, that is, water and a route for it. A chamber press works in batches and gives the driest cake, but the cycle ends with discharge, which means somebody has to be on site.

Wash water is a line in the water balance of the scheme, not a detail: for the belt press it is stated in the specifications alongside capacity and power — 11.2 m³/h for the model with a working belt width of 1000 mm. That water has to be supplied at the required quality, since solids blind the wash nozzles, and taken back together with the filtrate.

The mass of the machine and the space for discharge are settled in advance: one of the catalogue screw presses has an operating mass of 3400 kg and the chamber filter press with a filtration area of 100 m² weighs 6628 kg, and both need a floor of matching load-bearing capacity and enough height for the cake to drop straight into a skip. We do not manufacture this equipment: our work is the calculation by dry solids mass, the selection of the machine and the flocculant from a sludge sample, supply, commissioning and service.

Limits

When you need it

  • Treatment works with a flotation unit or a clarifier where sludge is produced continuously: at 94–97 % moisture it accumulates faster than it can be hauled away.
  • Biological treatment works producing surplus activated sludge that have no drying beds, or where drying beds are ruled out by sanitary or climatic conditions.
  • Plants where hauling liquid sludge has become a noticeable item of operating cost and grows along with output.
  • Production with sludge from chemical treatment — hydroxide or gypsum sludge — where the waste is classed as hazardous and the cost of handling it is charged by mass.
  • Sites where the contractor receiving the waste sets limits on its moisture or consistency.

When it will not help

  • Where sludge arises occasionally and in small quantity. The machine needs flocculant, washing and servicing regardless of its loading, and a holding tank with periodic haulage costs less.
  • Where the site cannot run the make-up and dosing of a polyelectrolyte solution. None of the three machines works without a flocculant, and the solution has to be prepared and matured, not tipped into the stream as dry product.
  • Where a moisture below what mechanical dewatering achieves is required. Going further is a matter for thermal drying: different equipment with a different order of energy consumption.
  • Where the task is to disinfect or stabilise the sludge. Dewatering reduces volume but does not stop the biological processes within the sludge; stabilisation or lime treatment is provided for that.
  • Where the works have nowhere to take the filtrate. Returning the separated water is a condition of the stage working at all, and no choice of machine resolves it.

Practice

Typical cases

Feed
Float from a food plant: about 8 m³/day at 95 % moisture (5 % dry solids), that is, some 400 kg of dry solids a day. The float is fatty and arrives in batches as the flotation scraper operates.
Task
Reduce the volume hauled away and stop shipping liquid sludge by tanker.
Scheme
Flotation unit → sludge holding tank with mixing → flocculant make-up and dosing station → screw press → skip for the cake; the filtrate returns to the balancing tank ahead of the flotation unit.
Result
At a cake moisture of 80 % the same 400 kg of dry solids occupy about 2 m³ a day instead of eight — a fourfold reduction, since the float was already comparatively concentrated. The holding tank is mandatory here: the press works to a steady flow while the flotation unit delivers in batches. The filtrate carries dissolved organics back, and its flow is included in the sizing of the balancing tank.
Feed
Surplus activated sludge from biological treatment works, thickened to 3 % dry solids: about 20 m³/day, that is, some 600 kg of dry solids a day. The sludge is light, gives up water reluctantly and changes with the seasons.
Task
Dewater the sludge on site within a single shift and return the filtrate to the head of the works at a known load.
Scheme
Secondary clarifier → thickener → holding tank → flocculant dosing → belt press → cake storage area; filtrate to the inlet chamber of the works.
Result
At a cake moisture of 82 % (18 % dry solids) the daily cake volume is about 3.3 m³ instead of twenty. Over a shift the wash water flow exceeds the daily sludge volume several times over and goes entirely into the filtrate: the return stream is appreciably larger by volume than the incoming sludge, and that is built into the sizing of the inlet chamber.
Feed
Hydroxide sludge from the chemical treatment of rinse water at an electroplating plant: about 4 m³/day at 3 % dry solids, containing metal compounds, the waste classed as hazardous.
Task
Obtain a cake of the lowest practicable moisture, since the cost of handling hazardous waste is charged by mass.
Scheme
Chemical treatment → clarifier → thickener → chamber filter press with a flocculant dosing station → packing of the cake; filtrate to testing and return into the chemical treatment.
Result
The batch cycle is no obstacle here: sludge is produced predictably and the press runs one or two loads a shift. Mineral hydroxide sludge gives up water more readily than organic sludge, and the cake comes out drier than on continuous presses. In return an operator is needed for discharge, the filter cloth requires regular washing, and the filtrate has to be checked: its residual metal content decides whether it can be returned to the scheme.

The cases are typical examples, not site reports.

Innovations

Our developments for this stage

Scheme

Place in the scheme

Dewatering is never a stage in its own right: it always follows the unit where the sludge arises, and its calculation starts not from the capacity of the machine but from the quantity of dry solids the preceding stage produces per day. A holding tank with mixing is placed between the sludge source and the press: sludge arrives in batches — as the scraper operates, as the clarifier is pumped down, as surplus sludge is withdrawn — whereas the press works to a steady flow and to a shift pattern.

Thickening ahead of dewatering is frequently justified. The higher the dry solids concentration at the inlet, the greater the dry solids throughput the machine takes at the same volume and the lower the flocculant consumption per tonne of dry solids; a gravity or mechanical thickener often makes a smaller size sufficient.

The flocculant make-up and dosing station enters the scheme as equipment of its own. Dry polyelectrolyte has to be dissolved, the solution matured and then diluted before it is introduced into the sludge stream; the concentration of the solution determines the actual dose, so it cannot be prepared without control.

Downstream of the press the scheme divides into two streams again. The cake drops into a skip or onto a storage area, which calls for height beneath the machine and access for vehicles. The filtrate returns to the head of the scheme, and its flow and composition enter the design of the main structures on the same footing as the incoming effluent.

Scheme

Automation and control

  • Flocculant dosing proportional to the sludge feed and referred to the inlet dry solids concentration. A fixed dose at variable flow means either excess reagent consumption or a breakdown of flocculation and carry-over of solids into the filtrate; with no in-line instrument the concentration itself is established by regular laboratory analysis rather than assumed constant.
  • Control of the pressing regime: screw speed and back-pressure cone position on a screw press, belt speed and belt tension on a belt press, end of cycle by the falling filtrate flow on a chamber press. These are the main settings by which cake moisture is adjusted on a machine already selected.
  • Washing of the filtering surfaces to a schedule: continuous on a belt press, intermittent on a screw press, between cycles on a chamber press. A missed wash shows up not at once but as a loss of capacity several days later.
  • Interlocks along the chain: a stopped drive has to stop the sludge feed and the flocculant dosing. Otherwise sludge keeps arriving at a stopped machine and reagent solution is consumed to no purpose.

Operation

Running it

Energy

The installed power of the continuous presses is modest: 1.65 kW in the catalogue screw presses and 1.1 kW of drive power in the belt presses. Referred to capacity, that gives of the order of 0.017 kWh per kilogram of dry solids on a screw press at its rated 100 kg DS/h and about 0.006 kWh per kilogram on a belt press at 200 kg DS/h. The specifications, however, state drive power, not the consumption of the whole unit: the sludge feed pump, the wash water pump, the solution make-up station and, on a chamber press, the high-pressure pump are supplied separately, and the total consumption is appreciably higher. Electricity is not the leading item here in any case: the operating cost of the stage is dominated by flocculant and by haulage of the cake.

Consumables

  • Flocculant (polyelectrolyte): the principal consumable of the stage. Consumption is referred to a tonne of dry solids rather than to a cubic metre of sludge; the grade and the dose are established by testing the actual sludge and revised when its origin changes
  • Wash water: on a belt press this is a continuous flow stated in the specifications (11.2 m³/h for the model with a working belt width of 1000 mm); on a screw press washing is intermittent and the volume much smaller; on a chamber press water is used to wash the cloth between cycles
  • Filtering elements: the belts of a belt press and the filter cloth of a chamber press. Their life is limited and depends on the abrasiveness of the sludge and the regularity of washing
  • Parts of the working element: moving and fixed rings and the screw on a screw press, rollers and bearing assemblies on a belt press, plate seals on a chamber press
  • Laboratory checks: inlet dry solids concentration, cake moisture, suspended solids in the filtrate. Without these three values the flocculant dose cannot be tuned

What goes to drain

The stage produces two streams and both call for a decision. The first is the cake: on continuous presses its moisture on most sludges falls within 75–85 %, and it is lower on a chamber filter press; the actual figure is set by the kind of sludge — mineral sludge gives up water more readily than organic — rather than by the type of machine as such. The cake is stackable, is loaded into a skip and hauled away; its hazard class and the permitted route are determined by the composition of the original effluent, not by the type of equipment. Mechanical dewatering does not stabilise sludge: in prolonged storage it putrefies, so the size of the storage area is limited by the haulage interval. The second stream is the filtrate: it returns to the head of the scheme carrying dissolved nitrogen and phosphorus, part of the COD and, where dosing is disturbed, carried-over fine solids as well. Its flow is close to that of the incoming sludge and, on a belt press, exceeds it by the volume of the wash water.

Sizing

Sizing

What we account for

  • Dry solids mass per day and the inlet dry solids concentration with the limits of its variation. A sludge volume quoted without a concentration is of no use for selection: it sets the hydraulics, while the loading of the machine is set by the dry solids
  • The origin of the sludge: surplus activated sludge, primary sludge, float, hydroxide sludge from chemical treatment. It governs the achievable cake moisture, the flocculant dose and the choice of sub-series
  • The duty of the site: the number of shifts and working days. The same daily output of dry solids is handled by a smaller size if the machine runs sixteen hours rather than eight
  • Requirements for the dewatered sludge: moisture, means of haulage, limits set by the receiving contractor
  • Availability of wash water of the required quality and the ability to take it back — for a belt press this is a line of the scheme's water balance in its own right
  • The ability of the main structures to accept the filtrate: its flow and its load in nitrogen, phosphorus and COD enter their design
  • The site: floor load-bearing capacity for the operating mass of the machine (3400 kg for one of the screw presses, 6628 kg for the chamber press with a filtration area of 100 m²), height for discharging the cake into a skip, vehicle access

What a wrong choice costs

  • Selecting on sludge volume without stating the concentration. A machine that takes 10 m³/h of sludge at 1.00 % dry solids will take about 2.5 m³/h of sludge at 4 %: the limit is on dry solids, not on volume. The error surfaces at commissioning and is corrected only by changing the size.
  • Sizing for round-the-clock operation with no time in reserve. The machine is stopped for washing, servicing and repair while sludge keeps arriving: if the daily output of dry solids equals the daily capacity, any stoppage overfills the holding tank.
  • The filtrate return not built into the design of the main structures. The return load increases sludge production, more sludge yields more filtrate, and the scheme settles at a regime other than the design one: it shows up as a rising load on the biological stage with no visible change in the incoming effluent.
  • A flocculant adopted by type of production rather than from a test. An unsuitable polyelectrolyte produces no floc at all: the sludge passes through the machine, the filtrate is turbid and there is no cake. This cannot be tuned by the dose — another grade is required.
  • Expecting a cake moisture below what is mechanically achievable. Bound water is not separated by mechanical pressure, and a requirement written into the brief without regard to the kind of sludge leads either to abandoning the stage or to buying a dryer that the design never allowed for.

Sizing

What we need for a calculation

  • The origin of the sludge and the stage at which it arises: float, clarifier sludge, surplus activated sludge, sludge from chemical treatment
  • Quantity: the dry solids mass per day, or the sludge volume together with the dry solids concentration without fail
  • A sludge analysis: dry solids concentration, pH, the organic share; for industrial sludge, the content of metals and petroleum products
  • The duty of the site: the number of shifts and working days per week, and whether staff are available for discharge operations
  • Requirements for the dewatered sludge: moisture, means of haulage, limits set by the receiving contractor
  • Where the filtrate goes, which structures accept it and what load they were designed for
  • The site: the room and its height, floor load-bearing capacity, power supply, wash water and its drainage, vehicle access to the skip, and whether a sludge sample can be provided for flocculant selection

Questions

Questions

Why is capacity stated in dry solids rather than in cubic metres per hour?

Because the machine is limited by the mass of solid phase it can separate, not by the volume of liquid passed through it. Sludge at 1.00 % dry solids holds about 10 kg of dry solids per cubic metre, so 10 m³/h of such sludge is 100 kg DS/h; the same machine on sludge at 5 % DS will take about 2 m³/h and deliver the same 100 kg DS/h. That is why the screw press specifications place the volumetric figure next to the concentration at which it was obtained: without it the figure carries no meaning.

Can sludge be dewatered without a flocculant?

No, and this is not a question of efficiency. Water is held by the extensive surface of fine particles, and the particles themselves are smaller than the filtering gap or the pores of the cloth. Until they are bound into large flocs they pass the filtering surface along with the water, blind it and leave with the filtrate, and no cake forms. The flocculant is part of the process on all three types of machine.

What cake moisture is achievable?

On continuous presses — screw and belt — it falls within 75–85 % on most sludges, and it is lower on chamber filter presses. The actual figure is set first of all by the kind of sludge: mineral and hydroxide sludges give up water more readily, surplus activated sludge least readily of all. The achievable moisture is established by testing rather than chosen from a data sheet, and below a certain limit mechanical dewatering does not proceed at all: bound water is separated only by thermal drying.

Screw, belt or chamber press — on what grounds is the choice made?

On the quantity of dry solids, on the duty of the site and on the required cake moisture. A screw press runs continuously at low speed, needs little wash water and tolerates swings in concentration — a solution for small and medium flows and for sites without a permanent operator. A belt press is also continuous and takes a larger flow, but requires continuous washing of the belts, that is, water and a route for it. A chamber press works in batches, gives the driest cake and ends its cycle with a discharge that calls for a person.

Where does the water separated from the sludge go?

It returns to the head of the treatment works. The filtrate is not clean water: dissolved nitrogen and phosphorus remain in it, along with part of the COD and, where dosing is out of order, carried-over fine solids. Its flow is close to that of the incoming sludge and, on a belt press, exceeds it by the volume of the wash water. The load of the return stream is taken into account when the main structures are designed; where that has not been done, the scheme runs away from its design regime.

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