plastic poster_final

1
ATR-ASSISTED ANALYSIS OF UNLABELED RECYCLABLES Faria Nusrat and Maria Vogt Division of Natural Sciences and Mathematics; Bloomfield College, Bloomfield, NJ 07003 U.S. Total Municipal Solid Waste Generation in 2012 Common Plastic Resin Profiles with Characteristic IR Frequencies Purpose Acknowledgements Metal/Glass/Paper to Plastic Resin Type Polymer FTIR-ATR Spectra CH 3 CH = CH 2 catalyst CH 2 CH(CH 3 ) Recycling statistics The Curious Case of Polystyrene Conclusions 1970s: beginnings of widespread plastic packaging and containers 2009: plastic packaging accounted for 30% of packaging sales 800 1000 1200 1400 1600 1800 2000 2400 2800 3200 3600 4000 1/cm 45 52.5 60 67.5 75 82.5 90 97.5 105 %T 2962.66 1714.72 1452.40 1408.04 1238.30 1116.78 1091.71 1041.56 1016.49 974.05 873.75 842.89 723.31 STD_ PETE_clear 800 1000 1200 1400 1600 1800 2000 2400 2800 3200 3600 4000 1/cm 45 52.5 60 67.5 75 82.5 90 97.5 105 %T 2914.44 2846.93 1471.69 1462.04 719.45 STD_ HDPE_white 800 1000 1200 1400 1600 1800 2000 2400 2800 3200 3600 4000 1/cm 65 70 75 80 85 90 95 100 105 %T 2949.16 2916.37 2868.15 2837.29 1454.33 1436.97 1375.25 1357.89 1166.93 972.12 STD_ PP_clear 800 1000 1200 1400 1600 1800 2000 2400 2800 3200 3600 4000 1/cm 80 82.5 85 87.5 90 92.5 95 97.5 100 102.5 %T 3059.10 3024.38 2920.23 1600.92 1492.90 1452.40 754.17 696.30 STD_ PS_clear CH 2 = CHCl catalyst CH 2 CH(Cl) Can IR be used to rapidly identify unlabeled plastics? Instrumentation: Shimadzu Affinity-1 Fourier Transform Infrared (FTIR) Spectrophotometer with Attenuated Total Reflectance Accessory (ATR) EPA, 2012: Almost 14 million tons as containers and packaging ~11 million tons as durable goods Almost 7 million tons as nondurable goods 9% of plastic waste (2.8 million tons) generated was recovered for recycling 28% of HDPE bottles and 31% of PET bottles & jars were recycled ~12% of bags, sacks, & wraps were recycled 251 Million Tons ethene CH 2 = CH 2 catalyst −[CH 2 CH 2 ] polyethylene propene polypropylene CH 2 = CH(Ø) catalyst CH 2 CH(Ø) styrene polystyrene Water, soft drink, juice bottles Balloons Soap and lotion bottles HDPE: Garbage bags Cleaning product containers Industrial products Personal care product containers LDPE: Shopping bags Dry cleaning bags Plastic food wrap Plumbing pipes Park benches Medical tubing Construction products Non-food bottles Window fittings Fencing Disposable cutlery, cups, bowls Packing peanuts Styrofoam containers Take-out food containers Automobile parts Laboratory Equipment “Microwave safe” food containers Carpeting and upholstery Toys FTIR Spectrum of Polystyrene without the ATR accessory FTIR Spectrum of Polystyrene with the ATR accessory (Note the large difference!) C=O Alkyl C-H C-Cl Alkyl C-H 800 1000 1200 1400 1600 1800 2000 2400 2800 3200 1/cm 88 90 92 94 96 98 100 102 %T 3059.10 3024.38 2920.23 1600.92 1492.90 1452.40 754.17 STD_ PS_clear 98 100 %T 1944.25 1869.02 1799.59 1734.01 This work was funded by the Independent College Fund of New Jersey (ICFNJ). We would like to thank Bloomfield College and Jim Flood (Shimadzu) for technical support. Mono-substituted aromatic IR can be used to rapidly identify unlabeled plastics HDPE and LDPE spectra are identical (difference is only their density) Unlabeled plastics greatly outnumber labeled plastics Most plastics are not recycled All plastics should be labeled AND recycled New labeling categories should be established for resins grouped in the “other” category Final Statement: Plastic consumption must be reduced and its recycling must be increased. CH 2 bend polyvinyl chloride vinyl chloride polyethylene terephthalate

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Page 1: Plastic Poster_Final

ATR-ASSISTED ANALYSIS OF UNLABELED RECYCLABLESFaria Nusrat and Maria Vogt

Division of Natural Sciences and Mathematics; Bloomfield College, Bloomfield, NJ 07003

U.S. Total Municipal Solid Waste

Generation in 2012

Common Plastic Resin Profiles with Characteristic IR Frequencies

Purpose

Acknowledgements

Metal/Glass/Paper to Plastic

Resin Type Polymer FTIR-ATR Spectra

𝑛CH3CH = CH2

catalyst− CH2CH(CH3) 𝑛 −Recycling statistics

The Curious Case of

Polystyrene

Conclusions

1970s: beginnings of

widespread plastic

packaging and containers

2009: plastic packaging

accounted for 30% of

packaging sales

80010001200140016001800200024002800320036004000

1/cm

45

52.5

60

67.5

75

82.5

90

97.5

105

%T

29

62

.66

17

14

.72

14

52

.40

14

08

.04

12

38

.30

11

16

.78

10

91

.71

10

41

.56

10

16

.49

97

4.0

5

87

3.7

58

42

.89

72

3.3

1

STD_ PETE_clear

80010001200140016001800200024002800320036004000

1/cm

45

52.5

60

67.5

75

82.5

90

97.5

105

%T

29

14

.44

28

46

.93

14

71

.69

14

62

.04

71

9.4

5

STD_ HDPE_white

80010001200140016001800200024002800320036004000

1/cm

65

70

75

80

85

90

95

100

105

%T

29

49

.16

29

16

.37

28

68

.15

28

37

.29

14

54

.33

14

36

.97

13

75

.25

13

57

.89

11

66

.93

97

2.1

2

STD_ PP_clear

80010001200140016001800200024002800320036004000

1/cm

80

82.5

85

87.5

90

92.5

95

97.5

100

102.5

%T

30

59

.10

30

24

.38

29

20

.23

16

00

.92

14

92

.90

14

52

.40

75

4.1

7

69

6.3

0

STD_ PS_clear

𝑛CH2 = CHClcatalyst

− CH2CH(Cl) 𝑛 −

Can IR be used to rapidly identify

unlabeled plastics?

Instrumentation:

Shimadzu Affinity-1

Fourier Transform

Infrared (FTIR) Spectrophotometer

with Attenuated Total Reflectance

Accessory

(ATR)

EPA, 2012:

• Almost 14 million tons as containers and

packaging

• ~11 million tons as durable goods

• Almost 7 million tons as nondurable goods

• 9% of plastic waste (2.8 million tons)

generated was recovered for recycling

• 28% of HDPE bottles and 31% of PET

bottles & jars were recycled

• ~12% of bags, sacks, & wraps were recycled

251 Million

Tons

ethene

𝑛CH2 = CH2

catalyst−[CH2CH2]𝑛 −

polyethylene

propene polypropylene

𝑛CH2 = CH(Ø)catalyst

− CH2CH(Ø) 𝑛 −

styrene polystyrene

• Water, soft drink,

juice bottles

• Balloons

• Soap and lotion

bottles

HDPE:

• Garbage bags

• Cleaning product

containers

• Industrial products

• Personal care product

containers

LDPE:

• Shopping bags

• Dry cleaning bags

• Plastic food wrap

• Plumbing pipes

• Park benches

• Medical tubing

• Construction products

• Non-food bottles

• Window fittings

• Fencing

• Disposable cutlery,

cups, bowls

• Packing peanuts

• Styrofoam containers

• Take-out food

containers

• Automobile parts

• Laboratory Equipment

• “Microwave safe”

food containers

• Carpeting and

upholstery

• Toys

FTIR Spectrum of Polystyrene without the

ATR accessory

FTIR Spectrum

of Polystyrene with the ATR accessory

(Note the large difference!)

C=O

Alkyl

C-H

C-Cl

Alkyl

C-H

800100012001400160018002000240028003200

1/cm

88

90

92

94

96

98

100

102

%T

30

59

.10

30

24

.38

29

20

.23

16

00

.92

14

92

.90

14

52

.40

75

4.1

7

STD_ PS_clear

12751350142515001575165017251800187519502025

1/cm

88

90

92

94

96

98

100

%T

19

44

.25

18

69

.02

17

99

.59

17

34

.01

16

00

.92

15

83

.56

15

41

.12

14

92

.90

14

52

.40

13

71

.39

13

50

.17

13

27

.03

12

78

.81

STD_ PS_clear

This work was funded by the Independent

College Fund of New Jersey (ICFNJ). We

would like to thank Bloomfield College and

Jim Flood (Shimadzu) for technical support.

Mono-substituted

aromatic

• IR can be used to rapidly identify unlabeled

plastics

• HDPE and LDPE spectra are identical

(difference is only their density)

• Unlabeled plastics greatly outnumber labeled

plastics

• Most plastics are not recycled

• All plastics should be labeled AND recycled

• New labeling categories should be established

for resins grouped in the “other” category

Final Statement: Plastic consumption must be

reduced and its recycling must be increased.

CH2 bend

polyvinyl chloridevinyl chloride

polyethylene terephthalate