• No results found

Techno-economic and ecological evaluation of a wood biorefinery

N/A
N/A
Protected

Academic year: 2021

Share "Techno-economic and ecological evaluation of a wood biorefinery"

Copied!
20
0
0

Loading.... (view fulltext now)

Full text

(1)

Techno-economic and ecological evaluation of a wood biorefinery

Martina Haase 1 , Magnus Fröhling 1 , Jörg Schweinle 2 , Birgit Himmelreich 3

1) Institute for Industrial Production, Universität Karlsruhe (TH)

2) Johann Heinrich von Thünen-Institute, Institute of Forest Based Sector Economics

3) Bayer Technology Services GmbH

Biorefinica 2009, January 27-28, DBU Osnabrück, Germany

Institute for Institute for Institute for Institute for

Industrial Production (IIP)

Industrial Production (IIP)

Industrial Production (IIP)

Industrial Production (IIP)

(2)

Content Content Content Content

 Introduction

 Methodology for the evaluation of process chains for biomass utilization

 Reference configuration of the modelled biorefinery

 Modelling of material and energy flows along the whole value chain

 Economic evaluation of the wood biorefinery

 Economic evaluation of the wood biorefinery

 Ecological evaluation of the wood biorefinery

 Summary

(3)

Increasing use of biomass in fossil based industries Increasing use of biomass in fossil based industries Increasing use of biomass in fossil based industries Increasing use of biomass in fossil based industries

 Replacement of limited fossil raw materials

 Increasing prices for non-renewable raw materials

 Reduction of dependency on crude oil imports and securing of raw material supply

 Reduction of greenhouse gas emissions

⇒ Increase of competition for biomass and arable land through new biomass utilization concepts

⇒ Enhancement of research and development regarding new conversion

technologies

(4)

Lignocellulosic Biomass

Disintegration, Separation

Cellulose Hemicellulose Lignin

Enzymatic conversion

Glucose Xylose

Phenol- Chemical

conversion

Furfural

Feedstock Precursors Platform

chemicals

Possible process steps and potential products of a wood biorefinery Possible process steps and potential products of a wood biorefinery Possible process steps and potential products of a wood biorefinery Possible process steps and potential products of a wood biorefinery

Wood chips Bark

Possible solvents:

-

Ethanol/Water

-

Ionic Liquids

-

H

2

SO

4

Phenol- derivatives Potential material

utilisation, e.g.

-

Binding agents

-

Fillers

-

Polymer compounds

-

Pulp

-

Cellulose derivatives

e.g. chemical or enzymatic hydrolysis

Subsequent processing to various

products, e.g.

-

Fuel additives

-

Polyethylene

-

PLA

-

Acrylic acid

(5)

Objectives of the techno Objectives of the techno Objectives of the techno

Objectives of the techno----economic and ecological evaluation economic and ecological evaluation economic and ecological evaluation economic and ecological evaluation

 Estimation of production costs and environmental effects of a process chain for the use of biomass at an early stage of process development

 Determination of economic and ecological key parameters and their influence on the sustainability of the process chain

Identification of cost-effective and environmentally sound process configurations

 Identification of cost-effective and environmentally sound process configurations

(6)

Methodology for the evaluation of process chains Methodology for the evaluation of process chains Methodology for the evaluation of process chains Methodology for the evaluation of process chains

Modelling of material and energy flows along the whole value chain (e.g.: Material flow analysis, process simulation)

Determination of a reference configuration

Estimation of raw and auxiliary material flows, energy demand, waste streams, products and emissions for different scenarios

Estimation of environmental impacts

E.g. acidification, global warming potential, eutrophication, CED,

...

Estimation of investments and production costs

Investment related costs, operating costs, costs for

disposal, labor, ...

Sensitivity analysis

Location and logistics planning

Availability of raw materials, infrastructure, consideration of

different plant sizes,

...

(7)

Reference configuration of the modelled biorefinery Reference configuration of the modelled biorefinery Reference configuration of the modelled biorefinery Reference configuration of the modelled biorefinery

 Plant capacity: 400.000 t dry wood/year

 Load: 50 t dry wood/h (8000 h/year)

 Feedstock properties : Wood chips of residual wood (P100, 50% water content), 42 % cellulose, 29% hemicellulose, 24% lignin, 5% others

 Organosolv pulping: Ethanol/Water mixture (50/50) T = 180°C, p = 18bar

Ratio wood : solvent = 1 : 6

 Enzymatic conversion of cellulose: Conversion rate to glucose: 82%

Cellulase and beta-glucosidase enzymes

 Hemicellulose fraction: Solute hemicellulose fragments after

organosolv pulping are subsumed to xylose

 Final products: Main product: Glucose (solution ~16 mass-%),

Byproducts: Xylose (solution ~5 mass-%), lignin (dry)

(8)

Major process steps for the production of glucose from wood Major process steps for the production of glucose from wood Major process steps for the production of glucose from wood Major process steps for the production of glucose from wood

Disintegration Separation of components CO

2

, H

2

O,

solar radiation

EtOH, H

2

O T = 180°C p = 18 bar

Precipitation Filtration Centrifugation Forest

production

Biological production, Forest maint.

Wood harvest/

chipping

Transport

Lorry

Enzymatic hydrolysis

Glucose Xylose Lignin Solvent

recovery

Flash- Separator

Distillation

Cellulase

β- Glucosi-

dase

(9)

Modelling of material and energy flows along the whole value chain Modelling of material and energy flows along the whole value chain Modelling of material and energy flows along the whole value chain Modelling of material and energy flows along the whole value chain

 Umberto ® material and energy flow network

P9:Wood chips

P10: Lignin fraction P12: Em iss ions ,

waste m aterials

Transport Disintegration and separation of components

T10:T ransport

P12: Emissions , P2:Raw and

auxiliary materials P5: Cellulose fraction P15: Wood

T1: Di sintegration and separation of components P6: Energy P18: Solvent

P2:Raw and auxiliary materials P12: Emissions,

waste materials P6: Energy

P13: UPR

P7: Cellulose fraction

P8:Xylose P6: Energy

P25: Lignin T11: Dryer

P6: Energy

T8: Enzym atic conversion P2:Raw and

auxiliary materials

P3:Glucose

P12: Emissions , waste materials T4: Water addition

auxiliary materials

P12: Emissions , waste materials T12: Forest production

P2:Raw and auxiliary materials

P12: Emissions, was te materials

Forest production P6: Energy

(10)

Subnet „Disintegration and separation of components“ (Sankey Diagram) Subnet „Disintegration and separation of components“ (Sankey Diagram) Subnet „Disintegration and separation of components“ (Sankey Diagram) Subnet „Disintegration and separation of components“ (Sankey Diagram)

P2:Raw and auxili ary materials

T2: Disintegration reactor

P11: Suspension

T3: Solvent compression

P6: Energy

T6: Centri fuge/decanter P9: Lösung

P14: Residue

T9: Flash

T8: Lignin precipitation

P20

T13: Centrifuge/

decanter

P22

P24: Solution

T15: Distillation

P17:Sol vent mixture

P6: Energy

P30: Wood chips

P6: Energy

P8: Hemicellulose fraction

P10:Lignin fraction

P12:Effl uents

P4:Water P7: Solvent

P18: Solvent

P16: Steam

T5: Heat exchanger P13: Steam

Ethanol Water

Wood / -components

P12:Effl uents

T14: Cellulose washing

P2:Raw and auxili ary materials

T1: Pressure release/

decanter

P1: Residue P6: Energy

P31: Cellulose fraction

P2:Raw and auxiliary materials

P3 T4: Heat exchanger P5: Steam

P16: Steam

(11)

Methodology for economic analysis Methodology for economic analysis Methodology for economic analysis Methodology for economic analysis

 Determination of glucose production costs:

- Variable costs and credits

o Costs for raw and operating materials (wood chips, ethanol, water, enzymes)

o Energy costs (electricity, steam, cooling)

 Estimation of investments:

- +/- 30% accuracy

- Site infrastructure completely available and useable (outside battery limits neglected)

o Energy costs (electricity, steam, cooling)

o Costs for sewage disposal

o Credits for by-products (lignin as high grade product, xylose)

- Investment related costs (depreciations, taxes and insurance, reparation and maintenance, costs of capital)

- Labour costs

 Costs for sales, administration and research are not yet determined

(12)

Structure of costs and credits for the base scenario Structure of costs and credits for the base scenario Structure of costs and credits for the base scenario Structure of costs and credits for the base scenario

Water Wood EtOH Enzymes

Steam Cooling Electricity

Effluents Depr.

Tax./Ins.

Rep./Maint.

Labour Admin.

Capital costs

0 200 400

C o s ts [ /t G lu c o s e ]

Input materials Energy Invest. dep.

costs Other costs Credits

Lignin

Xylose

-400 -200

C o s ts [ /t G lu c o s e ]

(13)

Estimation of glucose production costs for different scenarios Estimation of glucose production costs for different scenarios Estimation of glucose production costs for different scenarios Estimation of glucose production costs for different scenarios

 Consideration of different wood : solvent ratios

 Requirement for economic efficiency: production costs << market price for glucose

~

~

~

~ Glucose Glucose Glucose Glucose market price market price market price market price

400

€/t Glucose

Input materials Energy

Invest. dep.

costs Other costs

Scenario Scenario Scenario

Scenario

-400

Base Base Base Base 2222 3333 4444

0

€/t Glucose

Credits

Production costs Market price glucose

(14)

Sensitivity analysis for the base scenario Sensitivity analysis for the base scenario Sensitivity analysis for the base scenario Sensitivity analysis for the base scenario

 Prices for wood chips and lignin mainly influence glucose production costs

-20 0 20 40 60 80

P ro d u c ti o n c o s ts v a ri a ti o n [ % ]

-80 -60 -40 -20

-50 -40 -30 -20 -10 0 10 20 30 40 50

Parameter variation [%]

P ro d u c ti o n c o s ts v a ri a ti o n [ % ]

Lignin price Wood chips price Ethanol price

Enzymes price Investment Steam price

(15)

 Methodology for life cycle assessment (LCA) according to the international standard DIN EN ISO 14040 and 14044

 Goal and scope definition and life cycle inventory analysis

- „Cradle to gate analysis“ including forest production (wood maintenance, wood harvest/chipping), wood transport and the biorefinery processes

- Integration of supply chains for the provision of energy and operating materials (ecoinvent v2.0 LCI database)

Methodology for ecological evaluation Methodology for ecological evaluation Methodology for ecological evaluation Methodology for ecological evaluation

(ecoinvent v2.0 LCI database)

 Selection of impact categories, e.g. global warming potential, acidification, eutrophication

 Life cycle impact assessment (e.g. allocation of emissions to the

corresponding impact categories and conversion to indicator values, e.g. CO 2

equivalents)

(16)

 Determination of proportions of particular process steps to the emission equivalents of selected impact categories (base scenario)

Ecological evaluation Ecological evaluation Ecological evaluation

Ecological evaluation –––– Examples (1) Examples (1) Examples (1) Examples (1)

50%

100%

Fuel provision (forest mainten., wood harvest)

Fuel combustion (forest mainten., wood harvest)

Provision of diesel fuel (wood transport)

Fuel combustion (wood transport)

Global warming Global warming Global warming Global warming

potential potential potential

potential Acidification Acidification Acidification Acidification Eutrophication Eutrophication Eutrophication Eutrophication

 Uncertainties for contributions caused by enzymes production especially for PO 4 -Eq.

0%

CO2 equiv. SO2 equiv. PO4 equiv.

Provision of electricity (process plant)

Provision of steam (process plant)

Provision of auxiliary materials for the process

plant (enzymes, ethanol, water)

(17)

 Comparision of indicator values (CO 2 - and SO 2 - equivalents) for different scenarios

 Different scenarios result in different conclusions for several impact categories

Ecological evaluation Ecological evaluation Ecological evaluation

Ecological evaluation –––– Examples (2) Examples (2) Examples (2) Examples (2)

SO2-Equivalents 70

kg SO2-Equiv./h

CO2-Equivalents 30

t CO2-Equiv./h

Prov. of auxiliary materials for the process plant (enzymes, ethanol, water) Provision of steam (process plant)

Provision of electricity (process plant) Fuel combustion (wood transport)

Provision of diesel fuel (wood transport) Fuel combustion (forest mainten., wood harvest) 0

Base scenario Scenario "wood for steam generation"

kg SO2-Equiv./h

0

Base scenario Scenario "wood for steam generation"

t CO2-Equiv./h

1 : 6 1 : 6

(18)

 Comparison of CO 2 - and SO 2 - equivalents of the biorefinery with the production of potential reference products

 Assumptions:

- Sugar from a sugar refinery as reference product for xylose and glucose

- Phenol from a phenol plant as reference product for lignin

 Consideration of different wood : solvent ratios

 Biorefinery causes lower environmental effects compared to the reference processes 1

Ecological evaluation Ecological evaluation Ecological evaluation

Ecological evaluation –––– Examples (3) Examples (3) Examples (3) Examples (3)

50 220

Lignin Xylose Glucose Sugar from sugar refinery Phenol from phenol plant 0

55 110 165

Biorefinery 1:6

Biorefinery 1:8

Biorefinery 1:4

Biorefinery 1:4opt

Reference processes

kg SO2 equiv./ h

0 25

Biorefinery 1:6

Biorefinery 1:8

Biorefinery 1:4

Biorefinery 1:4opt

Reference processes

t CO2 equiv./ h

1 1 1

1

Values for reference processes derived from the ecoinvent v2.0 LCI database Values for reference processes derived from the ecoinvent v2.0 LCI database Values for reference processes derived from the ecoinvent v2.0 LCI database Values for reference processes derived from the ecoinvent v2.0 LCI database

(19)

Summary Summary Summary Summary

 Development of new concepts for the non-energetic use of biomass, e.g. wood biorefineries producing platform chemicals

 Modelling of mass and energy flows of a wood biorefinery along the whole value chain for different scenarios

 Early-stage techno-economic and ecological evaluation for the identification of sustainable production processes

 Economic efficiency highly depends on prices for raw materials and the sales

 Economic efficiency highly depends on prices for raw materials and the sales price for lignin

 Further improvement of process design is necessary to enhance economic efficiency

 Steam and electricity generation are crucial for the extent of GHG emissions

 Analysis of different impact categories may lead to different conclusions

(20)

Thank you for your attention!

Thank you for your attention!

Thank you for your attention!

Thank you for your attention!

Hertzstr. 16 76187 Karlsruhe

Dipl.-Umweltwiss. Martina Haase +49 (0)721 608-4467

martina.haase@wiwi.uni-karlsruhe.de

Dr. rer. pol. Magnus Fröhling +49 (0)721 608-4400

magnus.froehling@wiwi.uni-karlsruhe.de Institute for

Industrial Production (IIP)

This work is part of the research project “Pilotprojekt Lignocellulose Bioraffinerie”, supported by

the Federal Ministry of Food, Agriculture and Consumer Protection (BMELV) and attended by

the FNR.

References

Related documents

Several autoregressive integrated moving average (ARIMA) models with different time steps are proposed to predict the occurrences of large scale earthquakes by fitting the

Teacher attitudes and beliefs about the value of technology in the classroom have a direct influence on technology integration while other factors (e.g., technology support

By comparing the ITT impact on financial savings held at the Green Bank against the impact on savings held in assets and other informal and formal financial savings vehicles, we

SS GRAVITY SEWER INFLUENT MANHOLE (FLUSH) CHAIN LINK FENCE 16' GATE DUKE LIGHT POLE FORCE MAIN EFFLUENT PIPE 1&#34; WATER SERVICE IN OVERSIZED FORD METER BOX ELECTRICAL RACK W/

CIAL AUCHAN NORD RUE DU TORPILLEUR SIROCCO 63100 CLERMONT FERRAND BD ST JEAN CCIAL GEANT CASINO LE BREZET. 63100 CLERMONT FERRAND 27 RUE

The abstraction dimension is the detail at which we consider agents acting for the normative system: at the higher abstraction level agents have no role, at the next abstraction

However, due to the limitation of these methods, they cannot be applied for solving fully fuzzy linear programming (FFLP) with unre- stricted fuzzy coefficients and fuzzy variables..