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    WASTEWATERTREATMENTPLANTINECOTEX

    INNOVATIONWITHSEQUENCINGBATCHREACTOR(SBR)

    MD. SAIDUR RAHMAN SAJIB

    T.T.H Pre-Registation No. 1651

    Supervised By : Dr. Zulhas Ahmed signature : .

    Head Of The Department of Wet Processing

    College Of Textile Engineering & Technology(CTET)

    Abstract: There are a lot of technology involve with waste water treatment. Ecotex is a

    composite textile mill which is using the latest technology to treat their waste water. This paper

    work considers the study of sequencing Batch Reactor (SBR) in waste water treatment plant. For

    this purpose , Ecotex is taken for study. This report also contain a short description of the various

    Hi-Tec process module involved with Ecotex wastewater treatment plant such as equalization

    tank, coagulation, flocculation, Ozonation, , extended aeration, sequencing batch reactor e.t.c .

    Thefeasibility of bench scale sequencing batch reactors (SBRs) in treating

    in Ecotex effluent is

    demonstrated at various influent chemical

    oxygen demands (CODs) ranging from 300 to over

    4,000 mg/L.The SBRs removed over 75% of the biodegradable fraction of

    the influent COD at a

    fixed react time of 5.5h. An easy to use process model is presented to

    predict the temporal

    variations of substrate, biomass, and dissolved oxygenconcentrations during the fill and react

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    periods in SBRs. The

    model satisfactorily predicted effluent COD and final biomass

    concentrations, as

    well as temporal variations of COD, biomass, and dissolved oxygen

    throughout the fill and react cycles. The study provides a user-friendly approach to access

    essential knowledge about SBR and the procedures to design SBR, including design

    requirements, facilities selection and its advantage or disadvantage . it also describe the latest

    Ozonator technology which is Used By Ecotex . The paper concludes that the result of SBR

    technology involved with Ecotex by some spreadsheet calculation.

    Keywords : Sequencing batch reactor(SBR) , Activated sludge , COD, BOD .

    Introduction

    The textile industry occupies an important

    place in the economy of Bangladesh and

    other developing countries. Textile

    processing consumes enormous quantity of

    water and chemicals for various operations

    like washing, dyeing, etc. The low

    efficiency of chemical operations and

    spillage of chemical cause, a significant

    pollution hazard and make the treatment of

    discharged wastewater a complex problem.

    Most of the wastewater treatment plants

    recently adopt methods of chemical

    precipitation and subsequent clarification.

    Ecotex is a fully automated company

    situated in the Chandra,Pollibydut,Gazipur.

    It is a Uk-Bangladesh joint venture

    company. It is a composite mill which have

    a fully automated control wet processing

    floor where a hue amount of water is used

    per day . the waste water is discharged

    through the waste water treatment plant pipe

    Into their plant . every day they discharge

    average 850 m3/day water . The water

    parameter just before entering the treatment

    plant are very high but after treatment this

    parameter comes down near to the drinking

    quality !! Actually they are using the

    repetition of chemical precipitation and

    subsequent clarification. On the other hand,

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    for using the SBR technology with latest

    ozonator technology they treat the water like

    this . The initial COD value is over 300

    mg/L but after treatment it comes down

    average of 5 mg/L . This is a waste water

    treatment plant which are using the physico-

    chemical method. This treatment plant is

    designed for treatment of 15 ton water per

    day . the cost of treating water is 15 BDT /

    m3

    .The BOD and COD value of the water

    is reduced because of the double chemical

    action . For this reason the water parameter

    after treatment is so good for the Ecotex .

    The water characteristics , Design criteria

    and constraints used in ecotex is given

    below

    Table 1 : water characteristics , constrains used in

    Ecotex ( provided by Ecotex )

    Parameters Unit

    Effluent BOD5

    mg/l

    Influent flow rate, Q Mgal/d

    Influent suspended solids, SSin

    mg/l

    Influent volatile suspended solids, VSSin

    mg/l

    Wastewater temperature oC

    Influent BOD5for each day mg/l

    Hydraulic detention time, h

    Food-to-microorganism ratio, F/M

    MLVSS/MLSS

    Kinetic coefficients: Biomass yield, YEndogenous decay coefficient, k

    d

    lb/lb

    d-1

    Average concentration of settled sludge mg/l

    Settled sludge specific gravityPercent of the reactor volume which willbe

    %

    decanted each day

    Liquid depth of SBR ft

    Sludge wasting per week

    Biological solids in effluent mg/l

    Percent of biodegradable in effluent %

    Methodology

    Plant layout

    Ecotex having the great design to treat water

    fully and eco-friendly . the total plant is

    divided into two part. One part for chemical

    treatment and another part is for biological

    treatment . these two combination makes

    Ecotex wastewater treatment plant more cost

    effective .

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    A typical flow diagram of this plant is given

    below -

    Raw water.

    Ozone coagulant & polymer

    supernant

    Figure 1 : Process flow sheet of waste water treatment plant in Ecotex .

    Process Description

    The various section of waste water treatment

    plant in Ecotex is given below shortly

    Screening & Equalization

    Screens are very simple materials having

    iron bars in the form of square grids.

    Effluent is allowed to pass through the grid

    when large and coarse solid materials are

    arrested by it allowing smaller particles and

    effluent to pass through. In some several

    grids are use with diminishing grid sizes. In

    Ecotex they are using two screen ,one

    manual Bar screen and another Mechanical

    bar screen which is the product of Herman

    company .

    Figure : Mechanical Bar Screen

    Equalization tank is a large chamber which

    is designed for retention time . The

    Manual +

    Mechanical Screen

    Flocculation

    tank 2

    Ozone

    contactIntermediate

    tank

    Sequence

    batch reactor

    Clarifier 1

    Equalisation

    tank

    Ozone

    contact tank 1

    Flocculation

    tank 1

    Aerobic

    digestertank

    Water

    discharge

    Clarifier 2

    Sludge

    disposal

    Filter press

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    equalization tank is specially built where air

    is blown by two blowers alternately round

    the clock on continuous basis. The purposes

    of equalization are to supply oxygen so that

    DO level increases and To mix various types

    effluents and To reduce the temperature of

    the Water .In Ecotex they are using blower

    provided by SSR blower

    .

    Figure : Equalization tank in Ecotex

    Ozonation for ozone contact tank

    Ozone technology is the latest technology for

    wastewater treatment plant . In this system the

    Air is purified into the Oxygen . the machine

    which is used for ozone technology is known as

    ozonator . This ozonator machine is worked as

    they took the air as their input and they mixed it

    with the water separate the ozone , which is

    being converted into the oxygen by spark

    method . this oxygen then goes into the ozone

    contact tank where the oxygen is mixed with the

    waste water

    .

    Figure: Ozone machine in ecotex

    In Ecotex there are 16 ozonator machine . this

    machines are patented under the Mark 5 , Nuvo .

    The 8 m/c is used for ozone contact tank 1 , and

    another 8 m/c is used for ozone contact tank 2 .

    The reaction for ozonator is given below -

    Ozone (spark method) oxygen

    The oxygen is carried out from the ozonator to

    the tank by the pump and diffused through the

    diffuser .

    The ozone technology is one of the greatest

    technology nowadays . it makes the water moresoften.

    Flocculation And Coagulation

    From the ozone contact tank the effluent is

    taken to a small tank which is also called

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    flash mixing tank of small retention time. In

    the flash-mixing tank coagulants like lime

    (Ca(OH)2) and flocculants like ferrous

    sulfate (FeSO4) are dosed. This is done for

    coagulation and removal of the total dye

    particles. The basic idea of adding coagulant

    is to bring together all the suspended and

    dye particles so that they can be precipitated

    out in the flash mixing tank and flocculation

    tank by coagulation and flocculation

    mechanism. The chemical re-action that

    occurs in the coagulation and flocculation

    process is shown be-low;

    CaO + H2O = Ca(OH)2

    The above reaction take place in flash

    mixing tank when lime reacts with water

    and we get calcium hy-droxide solution.

    This solution reacts with the ferrous sulfate

    solution, which as follows-

    Ca(OH)2 + FeSO4 = CaSO4 + Fe(OH)3 +FeSO4(Un-reacted) + Fe(OH)2

    Adequate quantity of poly-electrolyte

    polymer solution is dosed in the flocculation

    tank followed by flash mixing tank to

    enhance the process of color removal by the

    flocculation process. A substantial amount

    BOD and COD etc. are re-moved in the

    coagulation and flocculation process.

    Figure : Flocculator tank

    In Ecotex there are two flocculator tank .

    One being use after ozone tank 1 and

    another one is used after ozone tank 2 .

    Clarifier

    Clarifier is the big tank where the sludge is

    settled for its gravitation . there are two

    inclined sludge settler(clarifier) in the

    Ecotex . One being used after the

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    flocculation and onether one is used in the

    last stage . these two clarifier is linked with

    the aerobic digester where the sludge is

    stored

    .

    Figure : Clarifier

    Intermediate tank

    Intermediate tank is the where the water rest

    some time .

    Figure : intermediate tank

    Aerobic Digester

    Aerobic digester is the small tank where the

    sludge is stored for some times foe settling

    .In here sludge is settled down for its own

    mass and then it is taken out by the sludge

    conditioning tank .

    Filter Press

    Filter Press is the pressing machine where

    the sludge removes its water under pressure

    .The water is then backed to the equalization

    tank .In here the sludge are shaped into cake

    form . This sludge then taken out for

    dumping .

    SEQUENCING BATCH REACTOR (SBR)

    The sequencing batch reactor (SBR) is a fill-

    and draw activated sludge system for

    wastewater treatment. In this system,

    wastewater is added to a single or lagoon

    batch reactor, treated to remove

    undesirable components, and then

    discharged. Equalization, aeration, and

    clarification can all be achieved using a

    single batch reactor. To optimize the

    performance of the system, two or more

    batch reactors are used in a predetermined

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    sequence of operations . SBR are uniquely

    suited for wastewater treatment applications

    characterized by low or intermittent flow

    conditions. Currently, sequencing batch

    reactor (SBR) technology is a well-

    promoted and tested alternative, which has a

    relatively low cost and small footprint. The

    SBR process offers flexibility of operation,

    where the sequence of successive phases can

    be adjusted to create the required

    combination of the growth conditions for

    different groups of microorganisms to

    remove different contaminants from

    wastewater, i.e.:

    aerobic for COD removal only,

    aerobic/anoxic for COD/nitrogen removal

    aerobic/ anoxic/ anaerobic for

    COD/nitrogen/phosphorus removal.

    Figure: SBR layout

    In Ecotex they are using Lagoon SBR

    system , which contain three chamber .they

    are currently using two chamber ,Another

    one is used for testing water parameter by

    fish cultivation . The SBR system gives

    them a unique miracle to treat the waste

    water. After treatment the water parameter

    comes down near to the drinking water .The

    working procedure of SBR is given below-

    Influent wastewater generally passes

    through screens and grit removal prior to the

    SBR. The wastewater then enters a partially

    filled reactor, containing biomass, which is

    acclimated to the wastewater constituents

    during preceding cycles. Once the reactor is

    full, it behaves like a conventional activated

    sludge system, but without a continuous

    influent or effluent flow. The aeration and

    mixing is discontinued after the biological

    reactions are complete, the biomass settles,

    and the treated supernatant is removed.

    Excess biomass is wasted at any time during

    the cycle. Frequent wasting results in

    holding the mass ratio of influent substrate

    to biomass nearly constant from cycle to

    cycle. Continuous flow systems hold the

    mass ratio of influent substrate to biomass

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    constant by adjusting return activated sludge

    flow rates continually as influent flow rates,

    characteristics, and settling tank underflow

    concentrations vary. After the SBR, the

    batch of wastewater may flow to an

    equalization basin where the wastewater

    flow rate to additional unit processed can be

    is controlled at a determined rate. In some

    cases the wastewater is filtered to remove

    additional solids and then disinfected. The

    solids handling system may consist of a

    thickener and an aerobic digester. With

    SBRs there is no need for return activated

    sludge (RAS) pumps and primary sludge

    (PS) pumps like those associated with

    conventional activated sludge systems. With

    the SBR, there is typically only one sludge

    to handle. The need for gravity thickeners

    prior to digestion is determined on a case by

    case basis depending on the characteristics

    of the sludge. An SBR serves as an

    equalization basin when the vessel is filling

    with wastewater, enabling the system to

    tolerate peak flows or peak loads in the

    influent and to equalize them in the batch

    reactor. In many conventional activated

    sludge systems, separate equalization is

    needed to protect the biological system from

    peak flows, which may wash out the

    biomass, or peak loads, which may upset the

    treatment process. It should also be noted

    that primary clarifiers are typically not

    required for municipal wastewater

    applications prior to an SBR. In most

    conventional activated sludge wastewater

    treatment plants, primary clarifiers are used

    prior to the biological system. However,

    primary clarifiers may be recommended by

    the SBR manufacturer if the total suspended

    solids (TSS) or biochemical oxygen demand

    (BOD) are greater than 400 to 500 mg/L.

    Historic data should be evaluated and the

    SBR manufacturer consulted to determine

    whether primary clarifiers or equalization

    are recommended prior to an SBR for

    municipal and industrial applications.

    Equalization may be required after the SBR,

    Depending on the downstream process. If

    equalization is not used prior to filtration,

    the filters need to be sized in order to

    receive the batch of wastewater from the

    SBR, resulting in a large surface area

    required for filtration. Sizing filters to

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    Accept these batch flows is usually not

    feasible, which is why equalization is used

    between an SBR and downstream filtration.

    Separate equalization following the

    biological system is generally not required

    for most conventional activated sludge

    systems, because the flow is on a continuous

    and more constant basis. The SBR plant

    treats a wastewater stream from a

    commercial textile operation.

    Figure: SBR in Ecotex

    The influent characteristics for the SBR

    plant are shown in Table 2 and Table 3

    summarizes the physical design parameters

    of the Ecotex Waste water treatment plant.

    Table 2: SBR Influent CharacteristicsInfluent Parameter Value of Ecotex

    BOD5 147 mg/L

    TSS 98 mg/L

    TKN 34 mgN/L

    NO3 0 mgN/L

    Total Average Influent

    Flow

    30,000 m3/d (7.9 MGD)

    Total Average Peak Flow 49,000 m3/d (12.9

    MGD)

    Table 3: SBR Physical Design ParametersDesign Parameter Value of Ecotex

    The original cycle settings are shown in the

    center of Table 4. The design objectives for

    effluent and maximum MLSS in the reactor

    for the SBR plant are shown in Table 5.

    Trains 4

    Volume of Each Reactor 5,700 m3 (1.5 MGal)

    Reactor Volume Total 22,800 m3 (6.0MGal)

    Water Level 5.13m 6.5m (low/highwater levels)

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    Table 4: Cycle Settings for the Designed

    and Optimal SBR ProcessSBR Phases Phase length (minutes)

    Filling and mixing 45

    filling and aeration 45

    Aeration only 135

    Mix only (anoxic) 60

    Settling 60

    Decant 55

    Desludge 20

    Total cycle length 360

    Table 5: Desired Effluent Quality andMLSSParameter Design Objectives (mg/L)

    Effluent CBOD5 15

    Effluent TSS 20

    ffluent NH4 3

    Effluent NO3 15,10,5

    Maximum MLSS 3000

    Advantages of SBR

    Equalization, primary clarification (in

    most cases), biological treatment, and

    secondary

    Clarification can be achieved in a single

    reactor vessel.

    Operating flexibility and control.

    Minimal footprint.

    Potential capital cost savings by

    eliminating

    Clarifiers and other equipment.

    Disadvantages of SBR

    A higher level of sophistication is

    required (compared to conventional

    systems), especially for larger systems,

    of timing units and controls.

    Higher level of maintenance (compared

    to conventional systems) associated with

    more sophisticated controls, automated

    switches, and automated valves.

    Potential of discharging floating or

    settled sludge during the DRAW or

    decant phase with some SBR

    configurations.

    Potential plugging of aeration devices

    during selected operating cycles

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    Result & Discussion

    Water quality monitor

    Ecotex have their own lab where they test

    their own treated water. In here some

    research has done. Some treated water was

    taken from the plant. And after testing it into

    the Ecotex laboratory found these

    characteristics of the water-

    Table 6: Water quality parameter

    Costing

    Ecotex is a very cost effective textile mill.

    Their wastewater treatment plant is also a

    cost effective plant. They spend only 15

    BDT/m3 to treat their water. Here is a graph

    of cost in month November, 2009 to treat

    their water

    Subject Inleteffluent

    Outleteffluent

    Flow rate 40M /hr 40M /hr

    P 8-14 7-8BOD 400-600

    PPM

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    Figure: Total cost analysis in the month of November, 2009. (Provided by Ecotex)

    Conclusion

    This case study illustrates the benefits of

    simulation for evaluation and optimization

    of the operation of an SBR treating in

    Ecotex a high strength industrial wastewater.

    The waste water treatment plant in Ecotex

    using SBR save a lot of money. The

    operational

    Improvements indicated by the simulations

    were as follows:

    1. High effluent TSS concentrations in the

    baseline operation were due to inadequate

    settling time in the secondary clarifiers,

    2. The aeration stage in the baseline

    operation was far longer than necessary,

    consuming

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    Excess energy with no additional benefit,

    3. A reduction in the time for the aeration

    stage could be used to provide an anoxic

    stage to

    Promote denitrification, and

    4. The SBR treatment cycle could be

    optimized to meet the stringent effluent

    criteria for

    Average and peak flow conditions, as well

    as winter, spring and summer wastewater

    Temperatures, with the exception of the

    effluent NO3 at peak loading and 20C/68

    F.

    Acknowledgement

    The author would like to acknowledge all

    the stuff of Ecotex, Ecotex testing lab

    assistant, Ecotex document database lab,

    Asif Mohammad Sami (consultant and

    designer of Ecotex), Subrata Paul (Assistant

    Engineer) and all those people who help

    author to write this document.

    Reference

    Asif Mohammad Sami, Consultant , Euro-

    asiatic limited

    Subrata Paul, Engineer ,Ecotex .

    Dold P.L., Wentzel M.C., Billing A.E.,

    Ekama G.A. and Marais G.v.R. (1991)

    Activated sludge simulation programs:

    Version 1.0 Nitrification and

    nitrification/denitrification systems.Pub. By

    Water Research Commission, P/Bag X03,

    Gezina 0031, South Africa.

    Henze M., Grady C.P.L. (Jr), Gujer W.,

    Marais G.v.R and Matsuo T. (1987)

    Activated Sludge Model No.1. IAWQ

    Scientific and Technical Report No.1,

    IAWQ, London. 33pp.

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    Henze M., Gujer W., Mino T., Matsuo T.,

    Wentzel M.C., Marais G.v.R. and Van

    Loosdrecht (1999) Activated sludge model

    No. 2d. Wat. Sci. Tech., 39 (1), 165-182.

    Hydromantis Consulting Engineers, GPS-X

    Version 4.1.2 (June 2003)

    Hu Zhi-rong (2001). External nitrification

    biological nutrient removal activated sludge

    systemsdevelopment and modelling, Ph.D

    thesis, Dept. of Civil Engineering,

    University of Cape Town, South Africa.

    Unai Iriarte, (2003) Personal communication

    Wentzel M.C., Ekama G.A., Marais G.v.R

    (1992)Process and modeling of nitrification

    denitrification biological excess phosphorus

    removal systems - a review. Wat. Sci. Tech.,

    25 (6), 59 - 82.

    ALPHENAAR A (1994) Anaerobic

    Granular Sludge: Characterization and

    Factors Affecting its Functioning. Ph.D.

    Thesis, Agric. Univ. of Wageningen, The

    Netherlands. 61-72.

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