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PRESENTED BY:
Warren Batchelor
Associate Professor
BioPRIA, Monash University
Kirubanandan Shanmugam, Hamid Doosthosseini,
Swambabu Varanasi, Gil Garnier, Warren Batchelor
Recyclability of Nanocellulose
films
Applications of Nanocellulose
Packaging1 Oil and water separation2 Photo catalyst3
Gels for Biomedical
Applications5
Nanocellulose
based composites6
Nanocomposites as High
Performance Barrier7
Membrane4
1. K.Shanmugam et al, Cellulose, 2017,24, 7, 2669–2676.
2. Z. he et al, RSC Adv., 2016, 6, 21435-21438
5. Mendoza et al, J Colloid Interface Sci. 2018 1;509:39-46.
7. U.M. Garusinghe et al, Colloids and Surfaces A,540, 2018,233-241.
3. U.M. Garusinghe et al, Scientific Reports, 8, 2306 (2018)
4. V. Swambabu et al , Chemical Engineering Journal 265(1) 2015.
2
Barrier materials
Wax
Aluminium
Plastics
Limitation:
Poor barrier
properties
3
Overview of Barrier Materials
Aulin and Lindström, Biopolymer Coatings for Paper and Paperboard, John Wiley & Sons, Ltd, 2011, pp. 255-276
4
Nanocellulose – Potential Barrier
• Bio degradable
• Non toxic
• Extreme High Surface Area
• Crystallinity
• Tuneable surface for
functionalization
Martin Hubbe el al, Nano cellulose in Packaging: A Review, Bio Resources 12(1), 2143-2233.
5
Nanocellulose film preparation techniques
1. Casting and Solvent evaporation 2. Vacuum filtration
Filtration Separation Drying
3. Spray coating followed by Vacuum filtration
Processing time – 10 min – 24 hrs
Drying time -10 mins
Processing Time –10-27 mins
Beneventi, D., Zeno, E., & Chaussy, D. (2015)
Processing and Drying time – 72 hrs
Laboratory scale
6
Rapid Preparation of NC films
7
Objective
To recycle and reprocess the spray
coated NC film
– Evaluate barrier properties of Virgin and
recycled NC
– Investigate effect of recycling on strength
of NC
Vacuum Filtration
8
Sheet Preparation Process
(British hand
sheet maker)
Recycled NC
Film
Virgin NC
Film
• 600 g of 0.2 wt.% suspension  60 gsm sheet
• No retention aid/on filter paper
Comparison
Properties
9
Recycling of Nanocellulose
Before Recycling
69.8± 11.3 nm
After Recycling
69.6± 12.6 nm
0 50 100 150 200 250 300 350
0
5
10
15
20
25
30
35
Bin
Fibre diameter in nm
Virgin NC Fibres
0 50 100 150 200 250
0
5
10
15
20
25
30
Fibre Diameter in nm
Bins
Recycled NC Fibre
10
Apparent Density
650
670
690
710
730
750
770
790
810
830
850
80 90 100 110 120 130 140
ApparentDensityinKg/m3
Basis weight in g/m2
Virgin NC film
Recycled NC film
11
Barrier Properties of Virgin and Recycled NC
0
2E-11
4E-11
6E-11
8E-11
1E-10
1.2E-10
1.4E-10
1.6E-10
90 100 110 120 130 140
Watervapourpermeability
g.m-1.s-1Pa-1
Basis weight in g/m2
Virgin NC Film
Recycled NC Film
Air Permanence
Virgin NC Film < 0.003 µm/Pa.S
Recycled sheet - 0.0045 µm/Pa.S
12
Effect of Recycling on strength of NC
20
30
40
50
60
70
80
90
100
110
80 85 90 95 100 105 110 115 120 125
TensileIndexinNm/g
Basis Weight in g/m2
Virgin NC Film-Instron Method
Recycled NC film -Instron Method
Virgin NC film -Zero span
Recycled NC film - Zero Span
13
Effect of Recycling on Uniformity
0.1
0.3
0.5
0.7
0.9
1.1
1.3
1.5
0 5 10 15 20 25 30 35 40
RelativeIndex
Components in mm
117.6 g/m2 Recycled NC Film
128.7 g/m2 Recycled NC Film
110.7 g/m2 Recycled NC Film
102.7 g/m2 Recycled NC Film
100.5 g/m2 Virgin NC Film
14
Surface Topography- SEM Micrographs at 2µm
15
Virgin Film-Filter side Recycled Film-Filter side
Virgin Film-Free side Recycled Film-Free side
1
SEM Micrographs at 10 µm
16
Virgin NC Film Recycled NC Film
Optical Profilometry
17
1
Virgin Film Recycled Film
Optical Profilometry of Free side of NC Film and Recycled NC Film (50 X Magnification)
18
Measurement Technique Area examined Effect of Recycling compared to virgin fibres
SEM Measurement of Fibre
diameter
1 micron scale bar None
SEM Measurement of Film
Surface
2 micron scale bar Nothing conclusive
SEM Measurement of Film
Surface
10 micron scale bar None
Optical Profilometry roughness 100 x 90 microns None
SEM Measurement of Film
Surface
100 micron scale bar None
Film thickness 159 mm Diameter of film Higher thickness at the same basis weight (g/m2)
Zero-span strength Estimated 300 micron span length 30 % Less
PPF tester of optical uniformity 1-15 mm inspection areas
16-39 mm inspection areas
Decrease in uniformity at lower areas of Inspection
Increase in uniformity at higher areas of Inspection
Water Vapour Permeability 63.5 mm diameter circle of film Higher permeability
˜ Doubled WVP
Air permeability 50 cm2 sample Higher permeability: permeability increased above the
detection limit of the instrument.
Tensile strength via Instron
Method
100 mm test span 30 % less strength
Comparison with WVP of Synthetic Polymers
Barrier Polymers Water
Transmission Rate
(g/m2 day)
Average
Thickness of the
film (µm)
Water Vapour Permeability
(g/m.s.Pa) x 10-11
The NC Film Vacuum
Filtration (100 g/m2)
52.9 119.4 4.97
Recycled Cellulose film
from Spray coated NC
89.5 133 9.83
Polyethylene (PE) 16.8 18.3 0.1
Plasticized (PVC) 118.6 12.7 0.49
Aluminium Foil
2.4 18.3
0.014
LDPE
18 25
0.088
HDPE
9 25
0.044
PS 109 to 155 25 0.53 - 0.75
PP 6 25 0.029
19
Conclusions
 Low permeance of air and water vapour even after recycling
 Retained 70% of the tensile strength
 Agglomeration of fibres affects initial film formation, concluding that the fibres are
not completely broke down.
 Recycled sheet shows limited reductions in barrier performance
 Platform for sustainability to replace synthetic packaging
20
Acknowledgment
• Monash Centre for Electron Microscopy
• Melbourne centre for Nanofabrication for Optical Profilometry Investigation
• Australian Research Council – BAMI Hub Grant
PRESENTED BY:
Warren Batchelor
Associate Professor
BioPRIA, Monash University
Thank you

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Recyclability of Spray Coated Smooth Nanocellulose films as a potential sustainable alternative to synthetic packaging

  • 1. PRESENTED BY: Warren Batchelor Associate Professor BioPRIA, Monash University Kirubanandan Shanmugam, Hamid Doosthosseini, Swambabu Varanasi, Gil Garnier, Warren Batchelor Recyclability of Nanocellulose films
  • 2. Applications of Nanocellulose Packaging1 Oil and water separation2 Photo catalyst3 Gels for Biomedical Applications5 Nanocellulose based composites6 Nanocomposites as High Performance Barrier7 Membrane4 1. K.Shanmugam et al, Cellulose, 2017,24, 7, 2669–2676. 2. Z. he et al, RSC Adv., 2016, 6, 21435-21438 5. Mendoza et al, J Colloid Interface Sci. 2018 1;509:39-46. 7. U.M. Garusinghe et al, Colloids and Surfaces A,540, 2018,233-241. 3. U.M. Garusinghe et al, Scientific Reports, 8, 2306 (2018) 4. V. Swambabu et al , Chemical Engineering Journal 265(1) 2015. 2
  • 4. Overview of Barrier Materials Aulin and Lindström, Biopolymer Coatings for Paper and Paperboard, John Wiley & Sons, Ltd, 2011, pp. 255-276 4
  • 5. Nanocellulose – Potential Barrier • Bio degradable • Non toxic • Extreme High Surface Area • Crystallinity • Tuneable surface for functionalization Martin Hubbe el al, Nano cellulose in Packaging: A Review, Bio Resources 12(1), 2143-2233. 5
  • 6. Nanocellulose film preparation techniques 1. Casting and Solvent evaporation 2. Vacuum filtration Filtration Separation Drying 3. Spray coating followed by Vacuum filtration Processing time – 10 min – 24 hrs Drying time -10 mins Processing Time –10-27 mins Beneventi, D., Zeno, E., & Chaussy, D. (2015) Processing and Drying time – 72 hrs Laboratory scale 6
  • 7. Rapid Preparation of NC films 7
  • 8. Objective To recycle and reprocess the spray coated NC film – Evaluate barrier properties of Virgin and recycled NC – Investigate effect of recycling on strength of NC Vacuum Filtration 8
  • 9. Sheet Preparation Process (British hand sheet maker) Recycled NC Film Virgin NC Film • 600 g of 0.2 wt.% suspension  60 gsm sheet • No retention aid/on filter paper Comparison Properties 9
  • 10. Recycling of Nanocellulose Before Recycling 69.8± 11.3 nm After Recycling 69.6± 12.6 nm 0 50 100 150 200 250 300 350 0 5 10 15 20 25 30 35 Bin Fibre diameter in nm Virgin NC Fibres 0 50 100 150 200 250 0 5 10 15 20 25 30 Fibre Diameter in nm Bins Recycled NC Fibre 10
  • 11. Apparent Density 650 670 690 710 730 750 770 790 810 830 850 80 90 100 110 120 130 140 ApparentDensityinKg/m3 Basis weight in g/m2 Virgin NC film Recycled NC film 11
  • 12. Barrier Properties of Virgin and Recycled NC 0 2E-11 4E-11 6E-11 8E-11 1E-10 1.2E-10 1.4E-10 1.6E-10 90 100 110 120 130 140 Watervapourpermeability g.m-1.s-1Pa-1 Basis weight in g/m2 Virgin NC Film Recycled NC Film Air Permanence Virgin NC Film < 0.003 µm/Pa.S Recycled sheet - 0.0045 µm/Pa.S 12
  • 13. Effect of Recycling on strength of NC 20 30 40 50 60 70 80 90 100 110 80 85 90 95 100 105 110 115 120 125 TensileIndexinNm/g Basis Weight in g/m2 Virgin NC Film-Instron Method Recycled NC film -Instron Method Virgin NC film -Zero span Recycled NC film - Zero Span 13
  • 14. Effect of Recycling on Uniformity 0.1 0.3 0.5 0.7 0.9 1.1 1.3 1.5 0 5 10 15 20 25 30 35 40 RelativeIndex Components in mm 117.6 g/m2 Recycled NC Film 128.7 g/m2 Recycled NC Film 110.7 g/m2 Recycled NC Film 102.7 g/m2 Recycled NC Film 100.5 g/m2 Virgin NC Film 14
  • 15. Surface Topography- SEM Micrographs at 2µm 15 Virgin Film-Filter side Recycled Film-Filter side Virgin Film-Free side Recycled Film-Free side 1
  • 16. SEM Micrographs at 10 µm 16 Virgin NC Film Recycled NC Film
  • 17. Optical Profilometry 17 1 Virgin Film Recycled Film Optical Profilometry of Free side of NC Film and Recycled NC Film (50 X Magnification)
  • 18. 18 Measurement Technique Area examined Effect of Recycling compared to virgin fibres SEM Measurement of Fibre diameter 1 micron scale bar None SEM Measurement of Film Surface 2 micron scale bar Nothing conclusive SEM Measurement of Film Surface 10 micron scale bar None Optical Profilometry roughness 100 x 90 microns None SEM Measurement of Film Surface 100 micron scale bar None Film thickness 159 mm Diameter of film Higher thickness at the same basis weight (g/m2) Zero-span strength Estimated 300 micron span length 30 % Less PPF tester of optical uniformity 1-15 mm inspection areas 16-39 mm inspection areas Decrease in uniformity at lower areas of Inspection Increase in uniformity at higher areas of Inspection Water Vapour Permeability 63.5 mm diameter circle of film Higher permeability ˜ Doubled WVP Air permeability 50 cm2 sample Higher permeability: permeability increased above the detection limit of the instrument. Tensile strength via Instron Method 100 mm test span 30 % less strength
  • 19. Comparison with WVP of Synthetic Polymers Barrier Polymers Water Transmission Rate (g/m2 day) Average Thickness of the film (µm) Water Vapour Permeability (g/m.s.Pa) x 10-11 The NC Film Vacuum Filtration (100 g/m2) 52.9 119.4 4.97 Recycled Cellulose film from Spray coated NC 89.5 133 9.83 Polyethylene (PE) 16.8 18.3 0.1 Plasticized (PVC) 118.6 12.7 0.49 Aluminium Foil 2.4 18.3 0.014 LDPE 18 25 0.088 HDPE 9 25 0.044 PS 109 to 155 25 0.53 - 0.75 PP 6 25 0.029 19
  • 20. Conclusions  Low permeance of air and water vapour even after recycling  Retained 70% of the tensile strength  Agglomeration of fibres affects initial film formation, concluding that the fibres are not completely broke down.  Recycled sheet shows limited reductions in barrier performance  Platform for sustainability to replace synthetic packaging 20
  • 21. Acknowledgment • Monash Centre for Electron Microscopy • Melbourne centre for Nanofabrication for Optical Profilometry Investigation • Australian Research Council – BAMI Hub Grant
  • 22. PRESENTED BY: Warren Batchelor Associate Professor BioPRIA, Monash University Thank you

Editor's Notes

  1. There are few methods available for nanocellulose films for various functionality. Casting of the nanocellulose suspension is the most common technique at laboratory scale and it requires longest drying time for evaporation of solvent in the suspension. Vacuum filtration is the most method for making the films. It requires processing time from 10 mins to 4hours in the nanocellulose film and in the case of nanocomposite, it requires 24 hrs s for dewatering in the filateration process 3. Spray coating is recently reported to replace the filtration process , however after coating , the same filteration is used to removed the excess water formed sheet and it required time which is not reported in the literatue. Therefore, these methods have problem in the scale up , it requires alternative process for fabrication nanocellulose film