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THERMOCHEMICAL CONVERSION OF MARINE WASTE

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Page 1: THERMOCHEMICAL CONVERSION OF MARINE WASTE
Page 2: THERMOCHEMICAL CONVERSION OF MARINE WASTE

THERMOCHEMICAL CONVERSION OF MARINE WASTE

BIOMASS TOWARDS RENEWABLE FUELS AND CHEMICALS

Frederik Ronsse, 26 nov ‘21, Songdo, GUGC

DEPARTMENT OF GREEN CHEMISTRY AND TECHNOLOGY

RESEARCH GROUP - THERMOCHEMICAL CONVERSION OF BIOMASS

Page 3: THERMOCHEMICAL CONVERSION OF MARINE WASTE

MARINE WASTE BIOMASS & THERMOCHEMICAL CONVERSION

3

Thermochemical conversion

• High T

• Optionally high P

• Dry or wet conditions

Marine microalgae

Residues from cultivation

Macroalgae (seaweeds)

Residues from cultivation

Algal blooms

Biological conversionThermochemical

conversion

Feedstock type Wet biomass Dry biomass (mostly)

Selectivity High Low

Degree of conversion Moderate to low High

Reaction conditions <70°C, 1 atm 100-1200°C, 0 - 250 atm

Conversion speed Slow: minutes to hours Fast: seconds to minutes

Materials

Fuels

Chemicals

Energy

Page 4: THERMOCHEMICAL CONVERSION OF MARINE WASTE

PYROLYSIS: INTRODUCTION

4

BiomassLiquid

(bio-oil)

Solid

fraction

GasHeat

Principle of pyrolysis

• Decomposition of biomass by heating in an oxygen-free or oxygen-deficient environment.

• Only useful for dry biomasses

• Always results in 3 product fractions: non-condensable gases, condensable vapors (result in bio-oil or

pyrolysis oil) and char(→biochar)

• Product distribution can be controlled based on process conditions – different process types to be

distinguished:Type Temp

(°C)Vapor

residence time

Heat source Char yield (wt.%)

Liquid yield(wt.%)

Gas yield(wt.%)

Slow pyrolysis 300-500 5-30 min external/internal 35 % 30 % 35 %

Fast pyrolysis 500-600 1 s external 12 % 75 % 13 %

Torrefaction (partial

pyrolysis)

< 300 minutes external 80 % 5 % 15 %

Gasification > 750 10-20 s internal (oxygen addition)

10 % 5 % 85 %

Page 5: THERMOCHEMICAL CONVERSION OF MARINE WASTE

HYDROTHERMAL CONVERSION: INTRODUCTION

5

Principle of hydrothermal conversion

• Hot, compressed water has remarkably different physicochemical properties (i.e. Kw, e, r) compared to at

ambient T, P

• At T > 374°C and P > 22.1 MPa: No distinction between the vapor and liquid phase: a single, new phase

emerges, the so-called supercritical fluid (SCW)

Sub critical

Near critical

Supercritical

Source: Dahmen, 2015

Page 6: THERMOCHEMICAL CONVERSION OF MARINE WASTE

HYDROTHERMAL CONVERSION: INTRODUCTION

6

Principle of hydrothermal conversion

• Different conversion processes can be distinguished at different T, P yielding different product slates

• Ideal for the conversion of wet feedstock (→marine waste feedstocks), no drying necessary

Page 7: THERMOCHEMICAL CONVERSION OF MARINE WASTE

POTENTIAL USE OF THERMOCHEMICAL CONVERSION PRODUCTS

7

Benefits of thermochemical conversion products: flexibility of applications

Transportation fuelsChemicals

Biomass

Whole fractions (i.e. sugars, phenols)

Single compounds

Bio-oil Char

+

Heat & power

Biochar

Pyrolysis

Functional carbon materials

Gasification UpgradingExtraction BoilerTurbine,

diesel engineSolid fuel

Adsorptive medium

Catalyst support

Electrode materials

Reductans

HTC

HTL

Biomass Biomass

Page 8: THERMOCHEMICAL CONVERSION OF MARINE WASTE

8

BIO-OIL / BIOCRUDE

Page 9: THERMOCHEMICAL CONVERSION OF MARINE WASTE

10

• When used in soils (aggregated) maximum yield improvements of 20 to 120%

Potential mechanisms

• Increasing the soil organic matter

• Form a protective habitat for soil micro-organisms

• Increase of soil porosity (thus increasing soil water retention and soil aeration)

• Increase soil’s cation exchange capacity (reduces leaching of nutrients and fertilizer)

• pH-correction (on average +1 pH unit)

• N-fixation an interaction in N-cycle

• Absorption of herbicides, heavy metal and other plant-toxic compounds

BIOCHAR

Page 10: THERMOCHEMICAL CONVERSION OF MARINE WASTE

11

• In soil: biochar is highly recalcitrant (long

lifetime in soil)

• Slow mineralization both biotic and abiotic)

of biochar in soil: C-mineralization rate at

least one order of magnitude lower than

parent biomass (to half-life of > 1000 yr)

• Biochar is mainly composed out of C. That

carbon was originally taken up by plants

from the atmosphere.

• → Biomass growth + pyrolysis + biochar soil

amendment is a carbon negative process.0 0.1 0.2 0.3 0.4 0.5 0.7 0.8 0.9

O/C Atomic ratio

100

101

102

103

104

105

106

107

108

Ha

lf lif

e (

ye

ars

)

t½ > 1000 years 100 years< t½ < 1000 years t½ < 100 years

Reduction volatile C compounds

Increase of fixed-C

BIOCHAR

Page 11: THERMOCHEMICAL CONVERSION OF MARINE WASTE

12

BIOCHAR

• Biochar in electrical energy storage

In: IEA (2009)

• Electric double layer capacitor

• Electrode material requirements:

• High specific surface area

• High meso/microporosity to support ion diffusion

• Micropore diameter > ion diameter

• High electrical conductivity

• Hydrophilic surface

Activated biochars

• Na-ion batteries

• Anode material requirements:

• Low meso/microporosity: ion flux

is much lower than in

supercapacitors

• No microporosity: Li-ions

intercalate between graphene

sheets in graphite

• For Na: ultramicroporosity, Na

ions can’t intercalate in graphite

(dNa+ > dLi+)

High temperature biochars

Page 12: THERMOCHEMICAL CONVERSION OF MARINE WASTE

13

• 1. High water content → hydrothermal processes

• 2. High heteroatom content (N, S and O), high ash content

• Lopez Bareiro et al. 2016: 8 microalgae strains processed through HTL at 375°C

• Upgrading through HDO to remove N, S and O (400 ºC, 4 h, 20 wt % catalyst: Pt/Al2O3 and HZSM-5)

CHALLENGES IN USING MARINE BIOMASS

Species Yield N C H O S

Scenedesmus obliquus 50.6 6.3 73.2 8.9 8.1 0.3

Phaeodactylum tricornutum 54.3 5.8 73.4 9.1 7.8 1.0

Nannocholoropsis gaditana 54.3 5.2 74.7 9.9 8.5 0.4

Scenedesmus almeriensis 58.1 6.1 74.3 9.1 8.4 0.4

Tetraselmis suecica 45.6 6.1 74.0 9.0 7.7 0.9

Chlorella vulgaris 55.3 7.1 72.5 8.7 8.6 0.5

Porphyridium purpureum 47.1 6.8 73.9 8.2 8.7 0.7

Dunaliella tertiolecta 55.3 6.2 72.0 8.8 9.9 0.3

Page 13: THERMOCHEMICAL CONVERSION OF MARINE WASTE

15

• 1. High water content → hydrothermal processes

• 2. High heteroatom content (N and O), high ash content

CHALLENGES IN USING MARINE BIOMASS

Scenedesmus almeriensis

C H N S O* HHV H/C O/C

Biocrude oil 74.3 9.2 5.7 0.8 10.0 36.1 1.486 0.101

Uncatalysed dry 82.3 10.4 4.8 <0.1 2.4 41.1 1.516 0.022

wet 80.6 10.0 4.9 0.1 4.4 39.8 1.489 0.041

Pt/Al2O3 dry 82.7 11.0 4.2 0.2 1.9 41.9 1.596 0.017

wet 80.1 10.1 4.7 0.2 4.9 39.7 1.513 0.046

HZSM-5 dry 81.8 10.3 5.0 0.1 2.8 40.7 1.511 0.026

wet 83.2 10.3 3.5 0.1 2.9 41.1 1.486 0.026

Nannochloropsis gaditana

C H N S O* HHV H/C O/C

Biocrude oil 74.4 10.1 4.8 0.5 10.2 37.1 1.629 0.103

Uncatalysed dry 83.6 11.3 2.1 0.2 2.8 42.3 1.622 0.025

wet 81.4 10.9 2.3 0.1 5.3 40.8 1.607 0.049

Pt/Al2O3 dry 84.2 11.7 2.4 <0.1 1.6 43.2 1.667 0.014

wet 82.0 11.2 2.8 <0.1 3.9 41.6 1.639 0.036

HZSM-5 dry 83.7 11.2 2.4 0.1 2.6 42.3 1.606 0.023

wet 82.4 11.0 2.5 <0.1 4.0 41.5 1.602 0.036

Page 14: THERMOCHEMICAL CONVERSION OF MARINE WASTE

16

• 1. High water content → hydrothermal processes

• 2. High heteroatom content (N and O), high ash content

• 3. How to integrate in biorefineries for maximum value creation ?

CHALLENGES IN USING MARINE BIOMASS

Water

Biomass

Produc-

tion

Light

C source

Nutrients

Harvesting

Water and nutrients recycle

Valuableco-products(e.g. lipids,

amino acids)

CO2 richgas

Solid residue

BIOCRUDE OIL

Fractionation HTL

FUELS

Page 15: THERMOCHEMICAL CONVERSION OF MARINE WASTE

Frederik RonsseProf. dr. ir.

DEPARTMENT OF GREEN CHEMISTRY AND TECHNOLOGY

E [email protected]

T +32 9 264 62 00

www.ugent.be