1
Seshasayee Mahadevan Subramanya 1 , Phillip E. Savage 1 1 Chemical Engineering Department, Pennsylvania State University, USA Hydrothermal Liquefaction for Processing Municipal Solid Waste without Separation [email protected] 1 Purpose 1. Municipal Solid Waste specifically plastics pose a grave danger to the environment. Current sustainable technologies like recycling are limited by the need for separation of solid waste. 2. Biomass components of municipal solid waste have been previously broken down to bio-oil using Hydrothermal Liquefaction [1] . 3. Preliminary work from our lab has suggested that plastics as well are converted to oil using Hydrothermal Liquefaction. High yields and heating values (HHV) were obtained. Hypothesis: Hydrothermal Liquefaction provides a solution for utilizing Municipal Solid Waste to obtain oil and useful other by-products in an economically sustainable manner Objectives: Studying synergistic effects in mixtures of municipal solid waste using model compounds Explore the possibility of extracting recyclable components from HTL products [4] Extraction set up Binary mixture extracted Model Compounds: 1. Cellulose (Paper, Food) 1. Starch (Food) 2. Soy Protein (Food) 3. Stearic Acid (Food) 4. Lignin (Wood) 5. Polypropylene (Plastic) 6. Polyethylene Terephthalate (Plastic) 7. Polystyrene (Plastic) 8. Polycarbonate (Plastic) 11 ml reactor Sand bath Oil Product Aqueous Phase Solid residue Gas Products Biomass accounts for 60% of total MSW but provides bio-oil that has lower yield and heating values. Plastics account for only 13% of total MSW but provides higher yield and HHV values comparable to gasoline Waste Heating value of Oil from HTL (MJ/kg) Oil Yield (%) Food waste 35.8 45.3 [1] Paper 32.3 5.1 [1] Wood 34.3 27.5 [5] Plastic waste 41.12 60.1 Biomass waste Plastic waste Better quality of oil produced Higher quantity of oil produced Reduce the use of catalyst and the need for upgradation Source Cost ($/gallon) Oil from HTL process 4.38 [6] Commercial Gasoline 3 1. Favorable interactions observed between plastics and biomass mixtures result in increasing oil yield as well as decreasing plastic decomposition temperatures. 2. Synergistic interactions between plastics and biomass exceed the synergistic interactions in- between components of biomass/ plastics significantly in the sub-critical temperature regime. 3. Ionic reactions are attributed for the synergy caused by plastic components on biomass. 4. Substantial synergistic interactions are found between PPE, PET, PBC, and biomass model compound mixture (over 85.29, 71.09, 70.33 % increase in oil yield respectively). References: 1: Gollakota, A. R. K., Nanda Kishore, and Sai Gu. Renewable and Sustainable Energy Reviews 81 (2018): 1378-1392. 2: Agency, United States Environmental Protection, "Advancing Sustainable Materials Management: Tables and Figures," 2015 3: Peterson, A. A.; Vogel, F.; Lachance, R. P.; Fröling, M.; Antal, Jr., M. J.; Tester, J. W. Energy Environ. Sci. 2008, 1 (1), 32 4: Williams, Paul T., and Edward Slaney, Resources, Conservation and Recycling, vol. 51, no. 4, pp. 754 - 769, 2007 5: Pedersen, Thomas Helmer, I. F. Grigoras,, Iulia Maria Daraban, Claus Uhrenholt Jensen, S. B. Iversen et al. Applied energy 162 (2016): 1034-1041. 6: Pedersen, Thomas Helmer, Nick Høy Hansen, and Lasse A. Rosendahl., Biofuels, Bioproducts and Biorefining 12, no. 2 (2018): 213-223. Hydrothermal Liquefaction Fuel gas (gaseous phase) energy recovery Crude Oil (organic phase) energy recovery Recyclable products (all phases) 83 % of Municipal Solid waste contains carbonaceous components that can be converted to oil using Hydrothermal Liquefaction Process Conditions: Temperatures - 300 °C, 350 °C, 400 °C, 450 °C, Pressure: 25 MPa, Time: 30 mins Loading - 0.3986 g feedstock, 1.3 4.5 mL water (based on temperature) 2 This Study 3 Methods 4 Results and Discussion 4 Results and Discussion (contd.) HPLC peaks obtained for aqueous phase of PET at 400 ˚C HPLC peaks of ethylene glycol standard Peak at 8.98 Multiple Peaks at 8.43 and 7.81 The HPLC peaks obtained for aqueous phase of the HTL of PET indicates multiple components of which ethylene glycol is one. Further analysis is to be performed to quantify the same. Conclusion Addition of plastic to biomass increases the net oil yield obtained by 101.67 % (experimental vs. calculated) at 300 ˚C. This is attributed to significant synergistic interactions between plastic and biomass components. Value addition from the HTL co-products is expected to improve the process’ sustainability and economically viability 5 Conclusions HTL Density, static dielectric constant, and ion product (K w ) of water at 30 MPa as a function of temperature [3] . Density (Kg/m 3 ) log 10 K w Dielectric constant Commercialization: + water Biomass mixtures have high synergistic interaction at super-critical temperatures HTL of Biomass give low oil yields HTL of Plastics give high oil yields Plastic mixtures have high synergistic interaction at sub-critical temperatures Synergistic interactions are significant between plastics and biomass components specifically at sub-critical temperatures PPE, PET, PBC show significant synergistic interactions with biomass at 350 ˚C A) Oil yield from HTL of mixture of model compounds mimicking biomass in MSW C) Oil yield from HTL of mixture of model compounds mimicking municipal solid waste D) Oil yield from HTL of one plastic + biomass mixture that mimic the composition of MSW B) Oil yield from HTL of mixture of model compounds mimicking plastics in MSW Municipal Solid Waste Composition [2] (262 million tons) in 2015 Biomass Plastics

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Page 1: Hydrothermal Liquefaction for Processing Municipal Solid ......Hydrothermal Liquefaction for Processing Municipal Solid Waste without Separation sesha@psu.edu 1 Purpose 1. Municipal

Seshasayee Mahadevan Subramanya1, Phillip E. Savage1

1Chemical Engineering Department, Pennsylvania State University, USA

Hydrothermal Liquefaction for Processing Municipal Solid Waste without Separation

[email protected]

1 Purpose

1. Municipal Solid Waste specifically plastics pose a grave danger to the environment. Current

sustainable technologies like recycling are limited by the need for separation of solid waste.

2. Biomass components of municipal solid waste have been previously broken down to bio-oil

using Hydrothermal Liquefaction[1].

3. Preliminary work from our lab has suggested that plastics as well are converted to oil using

Hydrothermal Liquefaction. High yields and heating values (HHV) were obtained.

Hypothesis: Hydrothermal Liquefaction provides a solution for utilizing Municipal Solid

Waste to obtain oil and useful other by-products in an economically sustainable manner

Objectives:

• Studying synergistic effects in mixtures of municipal solid waste using model compounds

• Explore the possibility of extracting recyclable components from HTL products[4]

Extraction set upBinary mixture

extracted

Model Compounds:

1. Cellulose

(Paper, Food)

1. Starch (Food)

2. Soy Protein (Food)

3. Stearic Acid (Food)

4. Lignin (Wood)

5. Polypropylene

(Plastic)

6. Polyethylene

Terephthalate (Plastic)

7. Polystyrene (Plastic)

8. Polycarbonate

(Plastic)11 ml reactor Sand bath

Oil Product

Aqueous Phase

Solid residue

Gas Products

• Biomass accounts for 60% of total MSW but providesbio-oil that has lower yield and heating values.

• Plastics account for only 13% of total MSW but provideshigher yield and HHV values comparable to gasoline

Waste Heating value of Oil from HTL

(MJ/kg)

Oil Yield (%)

Food waste 35.8 45.3[1]

Paper 32.3 5.1[1]

Wood 34.3 27.5[5]

Plastic waste 41.12 60.1Biomass

waste

Plastic

waste

• Better quality of oil produced

• Higher quantity of oil produced

• Reduce the use of catalyst and

the need for upgradation

Source Cost ($/gallon)

Oil from

HTL process

4.38 [6]

Commercial

Gasoline

3

1. Favorable interactions observed between plastics and biomass mixtures result in increasing

oil yield as well as decreasing plastic decomposition temperatures.

2. Synergistic interactions between plastics and biomass exceed the synergistic interactions in-

between components of biomass/ plastics significantly in the sub-critical temperature regime.

3. Ionic reactions are attributed for the synergy caused by plastic components on biomass.

4. Substantial synergistic interactions are found between PPE, PET, PBC, and biomass model

compound mixture (over 85.29, 71.09, 70.33 % increase in oil yield respectively).

References:1: Gollakota, A. R. K., Nanda Kishore, and Sai Gu. Renewable and Sustainable Energy Reviews 81 (2018): 1378-1392.2: Agency, United States Environmental Protection, "Advancing Sustainable Materials Management: Tables and Figures," 20153: Peterson, A. A.; Vogel, F.; Lachance, R. P.; Fröling, M.; Antal, Jr., M. J.; Tester, J. W. Energy Environ. Sci. 2008, 1 (1), 324: Williams, Paul T., and Edward Slaney, Resources, Conservation and Recycling, vol. 51, no. 4, pp. 754 - 769, 20075: Pedersen, Thomas Helmer, I. F. Grigoras,, Iulia Maria Daraban, Claus Uhrenholt Jensen, S. B. Iversen et al. Applied energy 162 (2016): 1034-1041.6: Pedersen, Thomas Helmer, Nick Høy Hansen, and Lasse A. Rosendahl., Biofuels, Bioproducts and Biorefining 12, no. 2 (2018): 213-223.

Hydrothermal

Liquefaction

Fuel gas

(gaseous phase)

energy recovery

Crude Oil

(organic phase)

energy recovery

Recyclable

products (all

phases)

83 % of Municipal Solid waste contains carbonaceous components that can be converted to oil

using Hydrothermal Liquefaction

Process Conditions: Temperatures - 300 °C, 350 °C, 400 °C, 450 °C, Pressure: 25 MPa, Time: 30 mins

Loading - 0.3986 g feedstock, 1.3 – 4.5 mL water (based on temperature)

2 This Study

3 Methods

4 Results and Discussion

4 Results and Discussion (contd.)

HPLC peaks obtained for aqueous phase of

PET at 400 ˚CHPLC peaks of ethylene glycol standard

Peak at 8.98 Multiple Peaks at 8.43 and 7.81 The HPLC peaks obtained for aqueous phase of

the HTL of PET indicates multiple components

of which ethylene glycol is one. Further analysis

is to be performed to quantify the same.

Conclusion

✓ Addition of plastic to biomass increases the net oil yield obtained

by 101.67 % (experimental vs. calculated) at 300 ˚C. This is

attributed to significant synergistic interactions between plastic and

biomass components.

✓ Value addition from the HTL co-products is expected to improve

the process’ sustainability and economically viability

5 Conclusions

HTL

Density, static dielectric constant, and ion

product (Kw) of water at 30 MPa as a

function of temperature[3].

Den

sity

(K

g/m

3)

log 1

0K w

Die

lect

ric

con

stan

t

Commercialization:

+ water

Biomass mixtures have high synergistic interaction at

super-critical temperatures

HTL of Biomass give low oil yields HTL of Plastics give high oil yields

Plastic mixtures have high synergistic interaction at

sub-critical temperatures

Synergistic interactions are significant between

plastics and biomass components specifically

at sub-critical temperatures

PPE, PET, PBC show significant synergistic

interactions with biomass at 350 ˚C

A)

Oil

yie

ld f

rom

HT

L o

f m

ixtu

re o

f m

odel

com

pounds

mim

ickin

g b

iom

ass

in M

SW

C)

Oil

yie

ld f

rom

HT

L o

f m

ixtu

re o

f m

odel

com

pounds

mim

ickin

g m

unic

ipal

soli

d w

aste

D)

Oil

yie

ld f

rom

HT

L o

f one

pla

stic

+ b

iom

ass

mix

ture

that

mim

ic t

he

com

posi

tion o

f M

SW

B)

Oil

yie

ld f

rom

HT

L o

f m

ixtu

re o

f m

odel

com

pounds

mim

ickin

g p

last

ics

in M

SW

Municipal Solid Waste Composition[2]

(262 million tons) in 2015

Bio

mas

sP

last

ics