CHLOROPHENOLICS OXIDATION FROM PULP BLEACHING EFFLUENTS USING PHOTOCATALYSIS

Page 1

INDIA WATER WEEK 2013 SESSION

“WASTEWATER MANAGEMENT - RECYCLING AND REUSE” PAPER TITLE

“CHLOROPHENOLICS OXIDATION FROM PULP BLEACHING EFFLUENTS USING PHOTOCATALYSIS”

CONTRIBUTORS PARVEEN KUMAR, SATISH KUMAR, NISHI KANT BHARDWAJ e-mail: parveenenv@gmail.com AMITY UNIVERSITY HARYANA , GURGAON (MANESAR)


INTRODUCTION INTRODUCTION  Pulp bleaching  Use of chlorine – AOX (chloro-organics)  Pollution prevention measures:

  

Pulp bleaching technology improvement Biological treatment Advanced oxidation treatment

(Photocatalysis: UV/TiO2, UV/TiO2/H2O2 , UV/O3/TiO2 etc.)


OBJECTIVES OBJECTIVES  Characterization of chlorophenolics generated during bleaching of mixed hardwood kraft pulp using DEPD sequence.  Photocatalytic

oxidation

of

chlorophenolics

by

effluent treatment with UV/TiO2 and UV/TiO2/H2O2 processes.


EXPERIMENTAL EXPERIMENTAL  Mixed hardwood kraft pulp (K.N. 15)  ClO2 produced in-situ from NaClO2  pH adjusted: 1M H2SO4 / 1M NaOH solution  NaOH solution: alkaline extraction of pulp  Target brightness: 87% ISO with DEPD sequence  Chlorine demand (%) = K.N. × K.F.  Bleaching performed: 200 g O.D. pulp  TiO2 (Fisher Scientific): Anatase (99.97 wt.%), BET surface area - 26.11 m2/g, Particle size - 50-150 nm)


PHOTOCATALYTIC PHOTOCATALYTIC REACTOR REACTOR


RESULTS RESULTS AND AND DISCUSSION DISCUSSION ANALYTICAL CHARACTERISTICS OF THE EFFLUENTS D1 Stage

EP Stage

COD (mg/L)

813

673

BOD (mg/L)

212

168

BOD/COD

0.26

0.25

Color (mg/L Pt-Co)

980

1113

pH

3.3

10.5

AOX (mg/L)

18

15.3

Parameters


CHLOROPHENOLICS CHLOROPHENOLICS OXIDATION OXIDATION FROM FROM DD11 AND AND EEPP STAGE STAGE EFFLUENTS EFFLUENTS USING USING UV/TiO UV/TiO22 AND AND UV/TiO UV/TiO22/H /H22O O22PROCESSES PROCESSES

Chlorophenolics

Initial con. (µg/L)

Removal (%) UV/TiO2

UV/TiO2/H2O2

D1

EP

D1

EP

D1

EP

3-chlorophenol

0.11

1.35

92

56

97

64

4-chlorophenol

0.04

0.02

81

87

96

ND

2,6-dichlorophenol

0.04

ND

86

-----

ND

-----

2,5-dichlorophenol

0.13

0.61

93

89

89

92

2,4-dichlorophenol

0.01

0.02

84

92

91

ND

3,4-dichlorophenol

0.04

0.04

77

75

79

81

4-chloroguaiacol

1.56

4.39

58

52

65

59

2,4,5-trichlorophenol

0.09

0.07

86

87

93

97

4,5-dichloroguaiacol

4.12

6.00

47

46

54

55


CONTINUED…….. CONTINUED……..

Chlorophenolics 2,3,4-trichlorophenol 4,6-dichloroguaiacol 3,6-dichlorocatechol 3,5-dichlorocatechol 3,4,5-trichloroguaiacol 4,5,6-trichloroguaiacol 5,6-dichlorovanillin Tetrachlorocatechol 2,6-dichlorosyringaldehyde Total

Initial con. (µg/L)

Removal (%) UV/TiO2

UV/TiO2/H2O2

D1

EP

D1

EP

D1

EP

0.06 0.03 2.14 0.62 0.01 ND ND 0.25 ND 9.3

0.06 0.06 ND ND ND 0.05 0.06 0.18 0.22 13.1

79 ND 59 83 82 --------83 ----57

84 90 ------------ND 74 90 83 53

93 ND 66 91 ND --------88 ----64

95 95 ------------ND 78 ND 86 61


Removal (%) of chlorophenolics by chemical family for D1 stage effluent

Removal (%) of chlorophenolics by chemical family for EP stage effluent

CHLOROPHENOLICS CHLOROPHENOLICS

REMOVAL REMOVAL

BY BY

CHEMICAL CHEMICAL


Removal (%) of chlorophenolics by number of attached chlorine atoms for D1 stage effluent

Removal (%) of chlorophenolics by number of attached chlorine atoms for EP stage effluent

CHLOROPHENOLICS CHLOROPHENOLICS REMOVAL REMOVAL BY BY NUMBER NUMBER OF OF ATTACHED ATTACHED CHLORINE CHLORINE ATOMS ATOMS


CONCLUSIONS CONCLUSIONS 

The experimental findings show that TiO2 photocatalysis is an attractive technique for the oxidation of chlorophenolics from pulp bleaching effluents.

Higher pollutants removal efficiency was achieved with UV/TiO2/H2O2 process as compared with UV/TiO2.

The biodegradability of the effluents improved after photocatalytic oxidation with both the processes. This indicates easy removal of the degradation products during biological treatment.

The photocatalysis, using solar light as an economical light source, may be a potential technology in future for remediation of biorecalcitrant pollutants.


THANK YOU


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