vii TABLE OF CONTENTS CHAPTER

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vii

CHAPTER

1

2

TABLE OF CONTENTS

TITLE

DECLARATION

DEDICATION

ACKNOWLEDGEMENT

ABSTRACT

ABSTRAK

TABLE OF CONTENTS

LIST OF TABLES

LIST OF FIGURES

LIST OF ABBREVIATIONS

LIST OF APPENDIX

INTRODUCTION

1.1 Background of Study

1.2 Statement of Problem

1.3 Objectives of Study

1.4 Scope of Study

1.5 Significance of Study

LITERATURE REVIEWS

2.1 Heavy Metal Pollution

2.2 Chromium

2.2.1 Chromium Chemistry and Its Speciation

2.2.1.1 Hexavalent Chromium

2.2.1.2 Trivalent Chromium

2.2.2 Chromium in Industries

PAGE ii vii xiii xv xix xxi iii iv v vi

2

3

1

3

4

6

6

5

7

9

11

3 viii

2.2.3 Chromium Toxicity

2.2.4 Chromium Transport and Accumulation

3.2.1 Growth of A. haemolyticus in NB and LB

medium

3.2.2 Cr(VI) Resistance by A. haemolyticus in

LB Medium

3.2.3 Cr(VI) Reduction by A. haemolyticus

12

13

2.2.6 Regulations of Chromium

2.3 Treatment Technologies for Cr(VI) Remediation

2.2.1 Conventional Methods

2.2.2 Biological Methods

2.2.2.1 Microbial Cr(VI) Reduction

2.2.2.2 Enzymatic Cr(VI) Reduction

2.2.2.3 Immobilization of Micobial Enzyme for

Cr(VI) Bioremediation

17

24

29

14

15

15

17

2.2.2.4 Support Materials for Enzyme

EXPERIMENTAL

Immobilization

31

3.1 Materials

3.1.1 Glassware

3.1.2 Acinetobacter haemolyticus

3.1.3 Culture Media

35

35

35

3.1.3.1 Nutrient Broth

3.1.3.2 Nutrient Agar Plates

3.1.3.3 Luria-Bertani Broth

3.1.3.4 Luria-Bertani Agar Plates

36

36

36

36

3.1.3.5 Luria-Bertani Cr(VI) Agar Plates

3.1.4 Maintenance of Bacterial Culture

37

37

37

37 3.1.5 Preparation of Active Culture

3.1.6 Spread Plate Technique

3.1.7 Chromium(VI) Stock Solution

3.1.8 Buffer Solutions

3.2 Cr(VI) Resistance and Reduction by A. haemolyticus

38

38

38

39

39

39

40

3.2.3.1 Cr(VI) Reduction by Growing Cells of

A. haemolyticus

3.2.3.2 Cr(VI) Reduction by Resting Cells of

A. haemolyticus

3.2.3.3 Cr(VI) Reduction by Permeabilized

Cells of A. haemolyticus

3.2.3.4 Determination of Cr(VI) Concentration

3.2.3.5 Analysis of Total Chromium

3.2.4 Mechanism of Cr(VI) Reduction by A. haemolyticus using Instrumental Analysis

3.2.4.1 Field Emission Scanning Electron

Microscope coupled with Energy

Dispersive X – Ray (FESEM-EDX)

3.2.4.2 Fourier Transform – Infra Red (FTIR)

3.2.4.3 Transmission Electron Microscopy

(TEM)

3.2.4.4 Electron Spin Resonance (ESR)

3.3 Isolation and Characterization of Crude Enzyme from

A. haemolyticus

3.3.1 Sub-cellular Fractionation of A. haemolyticus

3.3.2 Enzymatic Assay

3.3.2.1 Protein Assay using Bradford Method

3.3.2.2 Chromate Reductase Assay

3.3.3 Localization of Chromate Reductase Activity of A. haemolyticus

3.3.4 Characterization of Chromate Reductase

Activity in Crude Enzyme (Crude-Cell Free

Extracts – CFE) of A. haemolyticus

3.3.4.1 Effect of pH on Crude Enzyme

Activity and Stability

3.3.4.2 Effect of Temperature on Crude

Enzyme Activity ix

40

44

44

45

43

43

45

42

42

43

41

41

47

46

46

46

46

47

47

4 x

3.3.4.3 Effect of Electron Donors on Crude

Enzyme Activity

47

3.3.4.4 Effect of Metal Ions, Metabolic

Inhibitor and Protein Denaturant

48

3.3.4.5 Time Course and Kinetic Studies 48

3.4 Preliminary Studies on Immobilization of Crude CFE of 49

A. haemolyticus for Cr(VI) Reduction

3.4.1 Screening of Support Matrices for

Immobilization of Crude CFE of A. haemolyticus

3.4.2 Optimization of Cr(VI) Reduction using Crude

49

50

Enzyme Immobilized in Ca-alginate Beads

3.4.2.1 Effect of Initial pH of Cr(VI)

3.4.2.2 Reusability of CFE-immobilized in

Ca-alginate beads

RESULTS AND DISSCUSSION

4.1 Cr(VI) Resistance and Reduction by

4.1.1 Growth of

medium

A. haemolyticus

A. haemolyticus

in NB and LB

4.1.2 Cr(VI) Resistance by A. haemolyticus in LB

51

51

50

50

52

Medium

4.1.3 Cr(VI) Reduction by A. haemolyticus

4.1.3.1 Cr(VI) Reduction by Growing Cells of

A. haemolyticus

4.1.3.2 Cr(VI) Reduction by Resting and

Permeabilized Cells of A. haemolyticus

4.1.4 Mechanism of Cr(VI) Reduction by

A. haemolyticus using Instrumental Analysis

4.1.4.1 FESEM-EDX Analysis

4.1.4.2 FTIR Analysis

4.1.4.3 TEM Analysis

4.1.4.4 ESR Analysis

57

59

55

55

59

61

64

66

xi

4.2 Isolation and Characterization of Crude Enzyme from

A. haemolyticus

4.3.1 Screening of Support Matrices for

Immobilization of Crude CFE of A. haemolyticus

4.3.2 Cr(VI) reduction using Crude CFE Immobilized

in Ca-alginate Beads

4.3.1.1 Effect of Initial pH

4.3.1.2 Effect of Agitation Speed, Reaction

Time, Bead’s Dosage and Initial Cr(VI)

Concentration

4.3.1.6 Reusability of CFE-immobilized in Ca-

alginate beads

4.3.3 Comparison between Free and Immobilized

Crude CFE for Cr(VI) Reduction

68

4.2.1 Localization of Chromate Reductase Activity of A. haemolyticus

68

4.2.2 Characterization of Chromate Reductase 70

Activity in Crude Cell-Free Extracts of A.

haemolyticus

4.2.2.1 Effect of Temperature on Cr(VI)

Reduction

70

4.2.2.2 Effect of pH on Activity and Stability of 71

Chromate Reductase

4.2.2.3 Effect of Electron Donors on Cr(VI) 72

Reduction

4.2.2.4 Effect of Metal Ions

4.2.2.5 Effect of Metabolic Inhibitor and

Protein Denaturant

4.2.2.6 Kinetic and Time Course Studies of 79

Chromate Reductase Activity

4.3 Preliminary Studies on Immobilization of Crude CFE of 84

A. haemolyticus for Cr(VI) Reduction

74

77

84

92

86

86

88

93

5 CONCLUSION AND RECOMMENDATION

5.1 Conclusion

5.2 Recommendation for Future Work

REFERENCES

APPENDIX xii

95

95

96

97

123

xiii

4.1

4.2

4.3

4.4 xiv

81 Kinetic Parameters (K m

and V max

) for Cr(VI) reduction by crude CFE of A. haemolyticus at different reaction time

Kinetic parameters (K m

and V max

) and optimum conditions for chromate reductase activity by crude cellfree extracts of various microorganisms

Beads Integrity after Chromate Reduction for Various

Matrices

Structural integrity for Ca-alginate beads (with and without immobilized crude CFE) at different pH values

83

85

87

xv

2.2

2.3

2.4

2.5

2.6

2.11

4.1

LIST OF FIGURES

TITLE FIGURE NO.

2.1

2.9

2.10

4.2

4.3

Compliance Status to the Environmental Quality

(Industrial Effluent) Regulations (Department of

Environment, 2010)

E h

–pH Profile for Chromium

Structure of (a) CrO

4

2-

ion and (b) Cr

2

O

7

2-

ion

Schematic Diagram of Toxicity and Mutagenicity of

Cr(VI), (modified from Vincent, 1994).

Possible mechanisms of enzymatic Cr(VI) reduction under aerobic and anaerobic conditions (Wang and Shen, 1995).

Methods of Enzymes Immobilizaion (Sato and Tosa,

2002)

Chemical structure of Na

+

alginate. G, guluronic acid; M, mannuronic acid (Smidsrod and Braek, 1990).

Chemicals structure of (a) chitosan and (b) the binding of metal anions on chitosan (Naja and Volaesky, 2011).

The overall reaction of PVA–alginate bead formation

Growth profile of A. haemolyticus in NB and LB medium

OD

600

(  ), CFU ( ) and LB medium; OD

600

(

), CFU

( )

Growth of A. haemolyticus in LB broth supplemented with 30 -200 mg/L of Cr(VI); (a) OD

600

and (b) CFU/mL

Survival of A. haemolyticus supplemented with 30 -200 mg/L of Cr(VI) in (a) LB broth and (b) LB agar at 24 hour, 48 hour and 96 hour

PAGE

6

8

9

13

26

29

31

32

33

51

53

54

4.11

4.12

4.13

4.14

4.7

4.8

4.4

4.5

4.6

4.9

4.10 xvi

Cr(VI) Reduction in LB medium for (a) abiotic and (b) biotic by A. haemolyticus

Cr(VI) reduction by Resting and Permeabilized Cells of A. haemolyticus

FESEM micrographs of A. haemolyticus cells grown in

LB broth (a, b) without Cr(VI) (control) and (c, d) with

100 mg/L Cr(VI); magnification (a, b) 10k and (c, d) 25k.

EDX spectra with elemental compositions of A. haemolyticus cells grown in LB broth (a) without Cr(VI)

(control) and (b) with 100 mg/L Cr(VI).

FTIR spectra of Acineobacter haemolyticus cells grown in

LB broth (a) without Cr(VI) (control) and (b) with 100 mg/L Cr(VI).

The cell wall structure and composition of gram-negative bacteria (a), peptidoglycan stucture (b) (Kotrba et al .,

2011) and a schematic diagram of Cr(VI)-bacterial cells;

Cr

6+

initially binds with functional groups of bacterial cell wall and then reduced to Cr

3+

(c) (Das and Guha, 2007).

TEM micrographs of A. haemolyticus cells grown in LB broth (a, b) without Cr(VI) (control) and (c, d) with 100 mg/L Cr(VI); bar represents 1000 nm - a and c, 100 nm – b and d; arrow represents chromium accumulation in the cell (membrane fraction and cytoplasm) and outside the cells.

ESR spectrum from a solid-state of A. haemolyticus incubated with 100 of mg/L Cr(VI) in LB broth after 48 hour; (a) K

2

Cr

2

O

7

, (b) CrCl

3

·6H

2

O and (c) sample

Proposed mechanism for Cr(VI) reduction by A. haemolyticus (Modified by Li et al ., 2008)

Chromate reductase activity in different cell fractions of

A. haemolyticus.

Effect of temperature on chromate reductase activity of

A.haemolyticus

56

58

59

61

62

64

65

67

68

69

70

4.15

4.16

4.17

4.18

4.19

4.20

4.21

4.22

4.23

4.24 xvii

Effect of pH on the activity and stability of Cr(VI) reductase from CFE; (a) specific chromate reductase activity and (b) percentage Cr(VI) reduction

Effect of electron donors on Cr(VI) reductase activity (a) total and specific chromate reductase activity, and (b)

Cr(VI) reduction

Effect of metal ions on chromate reductase activity, (a) specific chromate reductase activity and (b) percentage

Cr(VI) reduction .

Non-competitive inhibition of chromate reduction by Ag

+ salts. Crude CFE was assayed for the rate of reduction of

29 or 48 µM Cr(VI) in the absence or presence of 1-14 mM Ag

+

Effect of EDTA and azide, as protein denaturant and metabolic inhibitor, on Cr(VI) reductase activity in CFE of A. haemolyticus .

Specific chromate reductase activity of CFE for A. haemolyticus at different initial Cr(VI) concentrations and reaction time; (a) 3 min – 60 min and (b) 120 min – 360 min.

Effect of initial Cr(VI) concentration on chromate reduction (a) in the presence of 1 mM Co

2+

and (b)

Lineweaver–Burk plot for Cr(VI) reduction after 3 min.

Cr(VI) reduction by crude CFE of A. haemolyticus immobilized in various support matrices

Effect of Initial pH on Cr(VI) reduction of 48 µM of

Cr(VI) (5g wet weight beads, 24 hour reaction time) by crude CFE immobilized-alginate

Effect of Agitation Speed on Cr(VI) reduction of 48 µM of Cr(VI) (pH 3, 5g wet weight beads, 24 hour reaction time) by crude CFE immobilized-alginate

72

73

75

76

78

80

81

84

86

88

4.25

4.26

4.27

4.28

4.29 xviii

Effect of Reaction Time on the Cr(VI) Reduction of 48

µM of Cr(VI) (100 rpm, pH 3, 5g wet weight beads) by crude CFE immobilized-alginate

Effect of Bead Dosage on immobilized CFE-alginate of

48 µM of Cr(VI) (100 rpm, pH 3, 24 hour reaction time) by crude CFE immobilized-alginate

Effect of Cr(VI) concentrations on immobilized CFEalginate of 10 - 192 µM of Cr(VI) (100 rpm, pH 3, 24 hour reaction time) by crude CFE immobilized-alginate

Reusability studies of immobilized CFE-alginate beads of

48 µM of Cr(VI) (100 rpm, pH 3, 24 hour reaction time) by crude CFE immobilized-alginate

Total Activity and Cr(VI) Reduction of 10 - 192 µM of

Cr(VI) at 30 min reaction time by Free and Immobilized crude CFE on Ca-alginate

89

90

91

92

93

% kWh

L

M m

3 mg

NADH

NADPH ng

[Cr]

°C

µg

CFE

CFU

DPC

EDTA g h

K i

K m kPa

OD

600 ppm rpm v v/v

V max

LIST OF ABBREVIATIONS

- Percentage

- chromium Concentration

- Degree Celcius

- Microgram

- Cell free extract

- Colony forming unit

- 1,5 - diphenylcarbazide

- Ethylenediaminetetraacetic acid

- Gram

- Hour

- Dissociation constant for inhibitor binding

- Michaelis–Menten constant

- kilopascal

- kilo Watt hour

- Liter

- Molar

- Meter Cubic

- Miligram

- Nicotinamide adenine dinucleotide

- Nicotinamide adenine dinucleotide phosphate

- Nanogram

- Optical density at 600 nm

- Part Per Million

- Rotation per minute

- Volume

- Volume per volume

- maximum rate or maximum velocity xix

V o w w/v

λ

- initial velocity

- Weight

- Weight per volume

- wavelength xx

APPENDIX NO.

A xxi

LIST OF APPENDIX

TITLE PAGE

List of publications (journal/article/chapter in book/book), awards, paper presentation seminar and workshop during this project period (Jun 2010 to July 2012)

123

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