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Investigation of Thermo-Gravimetric Analysis (TGA) on Waste Tires and Chemical Analysis Including Light Hydrocarbon, Substituted Aromatics, and Polycyclic Aromatic Hydrocarbon (PAH) Eilhann Kwon Department of Earth and Environmental Engineering (HKSM) Columbia University, New York, NY, 10027 15th NAWTEC, MAY 21-23, 2007, Miami, FL

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Investigation of Thermo-Gravimetric Analysis (TGA) on Waste Tires and Chemical Analysis Including Light Hydrocarbon, Substituted

Aromatics, and Polycyclic Aromatic Hydrocarbon (PAH)

Eilhann KwonDepartment of Earth and Environmental Engineering (HKSM)

Columbia University, New York, NY, 10027

15th NAWTEC, MAY 21-23, 2007, Miami, FL

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Presentation Outline

• Introduction & Background• Experimental Setup• Previous work• Results• Conclusions & Future Work

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Objectives

• Characterize the thermal degradation mechanisms of a waste tire in the combustion and pyrolysis process

• Identify by-products from the thermal degradation of a waste tire

• Investigate air pollutant generation mechanism from the combustion and pyrolysis process

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Feasibility of Waste tires as fuel

Heating Value of Fuels*

Fuel Heating Value (Btu/lb) Peat 2,500-6,500Wood 6,500Coal 8,000-14,500

Gasoline 20,400Diesel 19,300

Tire 12,000-16,000

* Source: NIST Chemistry WebBook

OilofBarrelmillionyrBTUnquadrillio

lblbBTU

12/ 09.0

1029320000,15 6

≈≈

×××≈

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Assumption• Avg. Wt. of a waste tire: 20lbs• Experimental heating value of a waste

tire: 15,000Btu/lb• Waste Tire generation a year: 293million

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Introduction

Landfill/Stockpile• 75% Void Volume

– Needs high cost of tipping fees– Leads to extremely difficult conditions

for quenching tire fires– Causes the piercing the landfilling cover

• Non-biodegradability• Leachate

Waste tire generation (293 million waste tires in U.S.)1 waste tire / 1 person / 1 year

Utilization Alternatives(Combustion & Gasification/Pyrolysis)

LandfillStockpiles

LandfillStockpiles

CombustionPyrolysis

Recycle

Recycle

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Source: EPA & Rubber Manufacturer Association

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Overall Experimental Setup

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N2

80ml/min

20ml/min

Heated tubing (280oC)

Micro-GC & GC/MS

Mass Flow Controller

Certified gases (pure and mixtures)

Const. Temperature

Water circulation

O2 Air

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Experimental ConditionsCurrent conditions found in combustors

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Air atmosphere (21% O2, 79% N2)

Lean atmosphere (7% O2, 93% N2)

Gasification/ pyrolysis (100% N2)

Enriched atmosphere (30% O2, 70% N2)

Possible enhancements for higher efficiency

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Properties of a Tire

Cross section of a tire Main constituents of rubber(Approximately 60%)

C C

CH2

H3C

H2C

H

**

n

*

HC

CH

H2C

CH2

HC

CH

H2C

CH2

CHCH2

H2C

CH

HC

*

n

C C

CH2

H

H2C

H

**

n

Natural Rubber(Poly-Isoprene)

Butyl Rubber

Styrene-Butadiene Rubber (SBR)25 wt% of Styrene+75wt% of Butadiene

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Previous Work

Thermo-gram of SBR and IR in various atmospheres at 20oC/min heating rate

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SBR IR

Wei

ght L

oss F

ract

ion,

α[-

]

Wei

ght L

oss F

ract

ion,

α[-

]

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Location of Epoxyethane in the Region of the Decomposition Plateau

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Marco J. Castaldi and Eilhann Kwon, “Beneficial Use of Waste Tires: An Integrated Gasification and Combustion Process Design via Thermo-Gravimetric Analysis (TGA) of Styrene-Butadiene Rubber (SBR) and Poly-Isoprene (IR)”, EES , In pressing, 2007

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Characterization of Thermal Degradation of Tires

Temperature, [oC]

0 200 400 600 800 1000

Wei

ght L

oss,

[%]

0

20

40

60

80

100

100% N2 Atmosphere7% O2 & 97% N2

Air Atmosphere30% O2 & 70% N2

Heating rate: 10oC/min

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Volatilization + Oxidation

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SEM/EDX Analysis

1000oC in N2 500oC in lean air 700oC in lean air 1000oC in lean air

Temperature (oC) Atmosphere C Wt % S Wt%25oC air 94.14% 2.6%

1000oC N2 93.19% NA500oC 7% O2 & Bal. N2 93.48% NA700oC 7% O2 & Bal. N2 88.15% NA

1000oC 7% O2 & Bal. N2 31.42% NA

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Chromatogram from a Tire at 400oC in N2 Atmosphere

Chromatogram from SBR Chromatogram from IR

Chromatograms from the thermal degradation of a Tire

Isoprene

Toluene EthylbenzeneStyrene

Styrene

1-methyl-4-(1-methylethyl)-benzene

Limonene

Limonene

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Concentration Profiles of Styrene & Limonene

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Heating rate: 20oC/min

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Proposed Limonene Formation MechanismEquilibrium geometry based on Hartree-Fock approximations using the 3-21G method

Modeling using SPARTAN, Wavefunction Inc.

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Chromatogram from IR in N2 Atmosphere

Isoprene

Limonene

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Qualitative GC/MS Results from a tire in Air

Chemical Species (M.W) Chemical Species (M.W)

Methane (16) 2-methyl-1-buten-3-yne (66)

Acetylene (26) Octane (114)

Ethane (30) 4-octene (112)

Propane (44) n-dodecane (170)

n-Butane (58) Ethanol (46)

But-1-ene (56) Cyclohexanol (112)

1,3-butadiene (54) 1-pentanol (88)

Pentane (72) 1-cyclopropyl-ethanone (84)

1-pentene (70) Octanal (142)

1,4-pentadiene (68) Propanone (142)

Hexane (86) Acetone (58)

1-Hexene (84) 2-Decanol (158)

Cyclohexene (82) 1,3-Butadienal (68)

1,1-dimethyl-cyclopropane (72) 3-Butene-2-one (70)

3-methyl-2-pentene (84) Buanone (72)

2-methyl-1-pentene (84) Hexanol (102)

1-methyl-cyclopentene (82) 3-Methyl Butanol (88)

4-methyl-cyclopentene (82) Thiophene (84)

Cyclopentene (68) Benzoic Acid (122)

2-pentyne (68) Benzaldehyde (106)

Hydrocarbons

Partial OxidationAlcohol

Aldehyde

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Concentration Profiles of Phenol in Various Atmospheres

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Concentrations of Chemical Release from a TGA Unit with a Tire at heating rate 10oC/min in air

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Concentration Profiles of Phenyl-C2-3 and Phenyl-C4from a tire in 30% O2 and Bal. N2 Atmosphere

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Precursors to the formation of PAHStructure breakdownGas phase addition of reactive

intermediates

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Hexylbenzene

1,2,4-triethylbenzene

1,3,5-triethylbenzene

Concentration Profiles of Phenyl-C6 from a tire in 7% O2 and Bal. N2 Atmosphere

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The Origin of Benzene DerivativesMain pathway to form benzene derivatives from SBR

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The Origin of Benzene Derivatives

Diels-Alder Reaction

From the thermal degradation of IR

Diels-Alder ReactionFrom SBR backbone

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Concentration Profiles of Naphthalene with a Tire in Various Atmospheres

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CH3

H3C

CH3

H3C

H3C

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Concentration Profiles of 2 and 3 ring at 10oC/min Heating Rate in Air Atmosphere

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Conclusions

• Volatilization and combustion was observed simultaneously when oxygen presented.

• The bond scission followed by hydrogenation was observed in monomer of main constituents of a tire

• The Hierarchical step for growing benzene derivatives by gas phase addition also observed.

• The oxidized benzene derivatives such as phenol reached up to 30PPMV in enhanced air atmosphere and the secondary oxidized chemical species derived from phenol such as benzaldehyde were observed.

• Oxidation is the feasible way to reduce the level of hazardous air pollutants including VOCs and PAHs.

• The chemical analysis from different ratio between SBR and IR in various atmospheres should be carried out.

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Future Work

• Determine and develop the higher efficiency and lower emission firing technology.

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AcknowledgementMarco J. Castaldi

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