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TREATMENT OF TEXTILE
             INDUSTRIAL
             W ASTEWATER
              FROM WATER JET LOOM
             MACHINE


Khanittha Charoenlarp
Rajamangala University of Technology Krungthep
Thailand.
Introduction

   The textile industry is a very diverse and
    broad manufacturing sector.

       Yarn production.
       Fabric production.
       Finishing.
       Fabrication.
Yarn production




carding            spinning
Fabric production



                Weaving




          Knitting
Finishing




Bleaching               Dyeing




 Printing               Finishing
Fabrication
Introduction
 W  eaving is one of the primary methods
  of textile production.
 It involves interlinking a set of vertical

  threads with a set of horizontal threads.
Weaving loom

                   Conventional loom




                Air jet loom   Water jet loom
rapier loom
Water jet loom
Water jet loom
   Advantage               Disadvantage
     Wide variety of         High amount of
      fiber and yarn           wastewater.
      types.                  Wastewater
     Widely used for          contaminate with
      apparel fabrics.         oil and sizing
     Decreasing of            agent.
      noise.
     Decreasing of
      damage yarn.
Introduction
   This sizing agent
       Polyvinyl alcohol
       Acrylic
       Lubricant substances

   The oily wastes
       Objectionable odors
       Undesirable appearance
       Toxic
       Limits oxygen transfer
W astewater Treatment in
Textile Industry
   Biological treatment
   Dissolved air floatation
   Coagulation-flocculation
   Membrane process
Coagulation Flocculation
   Chemical coagulants cause formation of
    a sludge phase that can be separated by
    density difference.

   Major coagulants:
       Al2(SO4) 3.14H2O (Alum)
       FeCl3.6H2O
       Fe2SO4
Destabilization
Electro-coagulation Defined:

Similar to Chemical Coagulation
Destabilize Charged Particles
Physical Removal (Settling)
Electro-coagulation can remove a wide
range of pollutants at the same time:

    suspended solids
    dyes
    emulsion
    organic matters
    heavy metals
Objective

   Investigating the efficiency of the method for
    treatment of wastewater from water jet loom
    machine by comparison between chemical coa
    gulation and electrocoagulation.
Method
   Analysis of wastewater from jet loom machine
   Chemical coagulation experiment
   Electrocoagulation experimental
1. Analysis of wastewater from jet loom
machine

•   The weaving wastewater from jet loom machine in
    Chonburee Province, Thailand was used in this
    study.

•   The properties of wastewater to be analyzed were
    turbidity, suspended solid (SS), total solid (TS), oil
    content and chemical oxygen demand (COD).
Measurements
      pH



               conductrometer


       turbidimeter
Measurements




               Dissolved solid and
                 suspended solid
2. Chemical coagulation
    experiment
   The influence factors of the chemical
    coagulation condition
       Type and amount of coagulant
       Type and amount of coagulant aids
       pH
       Stirring rate
Chemical coagulation
 Parameter
Condition                   Value
10% aq of coagulant (mL)    1.0,2.0,3.0,4.0,5.0 and
                            6.0
0.1% aq of coagulant aids   1.0,2.0 and 3.0
(mL)
pH                          4,5,6,7,8, and 9
Rapid stirring rate (rpm)   100, 120 and 150
Slow stirring rate (rpm)    30,60,90,120,150 and
                            180
3. Electrocoagulation
    Experimental
Electrocoagulation parameter


       Condition                  Value
Electrode material       Al and Fe
Electric potential (V)   20,25,30 and 35
Contact time (min)       30,60,90,120,150 and 180
Results

  Properties of wastewater from water jet loom
                     machine.
     Parameter        mean     SD     Standard
                                        Value
pH (25oC)             7.5    0.2      5.5-9
Turbidity (NTU)      188.7   4.1        -
COD (mg/  L)         1601.1 317.5      120
SS (mg/ L)           157.0 12.0        <50
TS (mg/ L)           2969.0 98.6      <3000
Oil content (mg/L)   571.8 64.8        5.0
The influence factors of chemical
coagulation

   F-test at 0.05 level of significance.

   Type and amount of coagulant, type and
    amount of coagulant aids, pH of solution and
    stirring rate were affected significantly with
    the efficiency of turbidity removal.
Effect of type and amount of coagulants


                                   88%




( ) 10% w/w aq Aluminum sulfate
( ) 10% w/w aq Ferrous sulfate
() 10% w/w aq Ferric chloride
Effect of pH
Effect of type and amount of coagulant aids




() 10%w/w aq aluminium sulfate + 0.01%w/w aq anionic polymer
() 10%w/w aq aluminium sulfate + 0.01%w/w aq cationic polymer
Effect of stirring rate
Effect of stirring rate
The influence factors of
electrocoagulation

     F-test at 0.05 level of significance.

     Electrode materials, Electric potential, and
      contact time were affected significantly with
      the efficiency of the turbidity removal.
Effect of electrode materials




() Aluminium electrode   () iron electrode
The effect of electric potential and
contact time




      () 20V ()25V ()30V   (x)35V
Conclusions

   The significant influence on the treatment
    efficiency of chemical coagulation.

       The type and amount of coagulant
       The type and amount of coagulant aids
       Initial of pH
       Stirring rate
Conclusions

   The significant influence on the treatment
    efficiency of electrocoagulation.

       Electrode material
       Electric potential
       Contact time
Optimum condition of chemical coagulation
                     method

   10% w/ of aluminum sulphate 80 mL and
           w
    0.01% w/ of cationic polymer 32 mL per 4 L of
             w
    wastewater.
   The mixture solution was rapidly stirred with 120
    rpm for 1 min and then slowly stirred with 20
    rpm for 20 min.
   The removal efficiency of turbidity, COD and oil
    content were 89%, 85% and 71%, respectively.
Optimum condition of
electrocoagulation method
   Aluminum electrode with 35 volts and 150
    min of contact time.

   The removal efficiency of turbidity, COD and
    oil content were 99%, 97% and 87%
    respectively.
Acknowledgement

   The authors would like to thank Rajamangala
    university of Technology Krungthep for the
    financial support and also grateful to
    Assist.Prof. Dr. Waraporn Tanakulrangsarn
    and Assist.Prof. Puangmanee Tantiwong for
    theirs valuable comments and suggestions.


      Thank you for your attention

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Treatment of Textile Industrial Wastewater

  • 1. TREATMENT OF TEXTILE INDUSTRIAL W ASTEWATER FROM WATER JET LOOM MACHINE Khanittha Charoenlarp Rajamangala University of Technology Krungthep Thailand.
  • 2. Introduction  The textile industry is a very diverse and broad manufacturing sector.  Yarn production.  Fabric production.  Finishing.  Fabrication.
  • 4. Fabric production Weaving Knitting
  • 5. Finishing Bleaching Dyeing Printing Finishing
  • 7. Introduction  W eaving is one of the primary methods of textile production.  It involves interlinking a set of vertical threads with a set of horizontal threads.
  • 8. Weaving loom Conventional loom Air jet loom Water jet loom rapier loom
  • 10. Water jet loom  Advantage  Disadvantage  Wide variety of  High amount of fiber and yarn wastewater. types.  Wastewater  Widely used for contaminate with apparel fabrics. oil and sizing  Decreasing of agent. noise.  Decreasing of damage yarn.
  • 11. Introduction  This sizing agent  Polyvinyl alcohol  Acrylic  Lubricant substances  The oily wastes  Objectionable odors  Undesirable appearance  Toxic  Limits oxygen transfer
  • 12. W astewater Treatment in Textile Industry  Biological treatment  Dissolved air floatation  Coagulation-flocculation  Membrane process
  • 13. Coagulation Flocculation  Chemical coagulants cause formation of a sludge phase that can be separated by density difference.  Major coagulants:  Al2(SO4) 3.14H2O (Alum)  FeCl3.6H2O  Fe2SO4
  • 15. Electro-coagulation Defined: Similar to Chemical Coagulation Destabilize Charged Particles Physical Removal (Settling)
  • 16.
  • 17. Electro-coagulation can remove a wide range of pollutants at the same time:  suspended solids  dyes  emulsion  organic matters  heavy metals
  • 18. Objective  Investigating the efficiency of the method for treatment of wastewater from water jet loom machine by comparison between chemical coa gulation and electrocoagulation.
  • 19. Method  Analysis of wastewater from jet loom machine  Chemical coagulation experiment  Electrocoagulation experimental
  • 20. 1. Analysis of wastewater from jet loom machine • The weaving wastewater from jet loom machine in Chonburee Province, Thailand was used in this study. • The properties of wastewater to be analyzed were turbidity, suspended solid (SS), total solid (TS), oil content and chemical oxygen demand (COD).
  • 21. Measurements pH conductrometer turbidimeter
  • 22. Measurements Dissolved solid and suspended solid
  • 23. 2. Chemical coagulation experiment  The influence factors of the chemical coagulation condition  Type and amount of coagulant  Type and amount of coagulant aids  pH  Stirring rate
  • 24. Chemical coagulation Parameter Condition Value 10% aq of coagulant (mL) 1.0,2.0,3.0,4.0,5.0 and 6.0 0.1% aq of coagulant aids 1.0,2.0 and 3.0 (mL) pH 4,5,6,7,8, and 9 Rapid stirring rate (rpm) 100, 120 and 150 Slow stirring rate (rpm) 30,60,90,120,150 and 180
  • 25. 3. Electrocoagulation Experimental
  • 26. Electrocoagulation parameter Condition Value Electrode material Al and Fe Electric potential (V) 20,25,30 and 35 Contact time (min) 30,60,90,120,150 and 180
  • 27. Results Properties of wastewater from water jet loom machine. Parameter mean SD Standard Value pH (25oC) 7.5 0.2 5.5-9 Turbidity (NTU) 188.7 4.1 - COD (mg/ L) 1601.1 317.5 120 SS (mg/ L) 157.0 12.0 <50 TS (mg/ L) 2969.0 98.6 <3000 Oil content (mg/L) 571.8 64.8 5.0
  • 28. The influence factors of chemical coagulation  F-test at 0.05 level of significance.  Type and amount of coagulant, type and amount of coagulant aids, pH of solution and stirring rate were affected significantly with the efficiency of turbidity removal.
  • 29. Effect of type and amount of coagulants 88% ( ) 10% w/w aq Aluminum sulfate ( ) 10% w/w aq Ferrous sulfate () 10% w/w aq Ferric chloride
  • 31. Effect of type and amount of coagulant aids () 10%w/w aq aluminium sulfate + 0.01%w/w aq anionic polymer () 10%w/w aq aluminium sulfate + 0.01%w/w aq cationic polymer
  • 34. The influence factors of electrocoagulation  F-test at 0.05 level of significance.  Electrode materials, Electric potential, and contact time were affected significantly with the efficiency of the turbidity removal.
  • 35. Effect of electrode materials () Aluminium electrode () iron electrode
  • 36. The effect of electric potential and contact time () 20V ()25V ()30V (x)35V
  • 37.
  • 38. Conclusions  The significant influence on the treatment efficiency of chemical coagulation.  The type and amount of coagulant  The type and amount of coagulant aids  Initial of pH  Stirring rate
  • 39. Conclusions  The significant influence on the treatment efficiency of electrocoagulation.  Electrode material  Electric potential  Contact time
  • 40. Optimum condition of chemical coagulation method  10% w/ of aluminum sulphate 80 mL and w 0.01% w/ of cationic polymer 32 mL per 4 L of w wastewater.  The mixture solution was rapidly stirred with 120 rpm for 1 min and then slowly stirred with 20 rpm for 20 min.  The removal efficiency of turbidity, COD and oil content were 89%, 85% and 71%, respectively.
  • 41. Optimum condition of electrocoagulation method  Aluminum electrode with 35 volts and 150 min of contact time.  The removal efficiency of turbidity, COD and oil content were 99%, 97% and 87% respectively.
  • 42. Acknowledgement  The authors would like to thank Rajamangala university of Technology Krungthep for the financial support and also grateful to Assist.Prof. Dr. Waraporn Tanakulrangsarn and Assist.Prof. Puangmanee Tantiwong for theirs valuable comments and suggestions. Thank you for your attention