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Waste to Energy Conference – 06-07/11/2017 – Istanbul, Turkey 1
Michael Köttner
Energy from Organic Waste – Biogas
Plants
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• Know-how transfer (international workshops, conferences, study
tours, training)
• Technical support especially with
dry digestion, lagoon technology,
small scale installations
• Contacts to experts in planning,
design and construction
• Contacts to specialized
companies
• Networking with members
in different regions, nationally
and internationally
Activities of IBBK related to biogas technology
2
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What is biogas?
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Methane CH4 50 – 80 %
Carbon dioxide CO2 40 – 50 %
Water Vapour H20 0 – 20 %
Nitrogen N2 0 – 10 %
Oxygen O2 0 – 2 %
Hydrogen sulphide H2S 0 – 1 %
Hydrogen (hydrolysis) H2 0 – 1 %
Ammonia NH3 0 – 1 %
Biogas definition
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Biogas definition
• Biogas is produced through the anaerobic degradation of organic
material by microorganisms
• Framework conditions for good production:
• Anaerobic condition → absence of air/oxygen
• The organic material must be readily available → no lignocellulose
• Sufficient moisture → at least 50 %
• Constant temperature (mesophilic: 38-42 °C, thermophilic: 50-55 °C)
• Constant feed quality
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Biogas usage methods
Source: Fachverband Biogas
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Feedstock for biogas production in Germany
2% 3%
44%
13%
48%
77%
6% 7%
% by weight % by energy input
Industrial and agricultural residues
Energy crops
Liquid and solid manure
Biowaste
7Source: Fachverband Biogas
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Biogas potentials of various bio-waste
Source: Fachverband Biogas
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Biowaste treatment technologies
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Process selection criteria
Utilization of biowaste
Material
Composting/Direct utilization
Material/Energetic
Anaerobic digestion
Energetic
Incineration
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Process selection criteria
Water content
Structure
Co
mp
ostin
g / D
ry F
erm
en
tatio
n
Garden waste
Household-waste (rural)
Household-waste (urban)
Kitchen waste
Food waste
Catering waste
Slaughterhouse waste
Organic industrial waste
We
t Fe
rme
nta
tion
tion
Source: Wiemer & Partner 1994
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Process comparisons
Wet fermentation Dry fermentation
Continuous processDiscontinuous/Batch process
Source: Fachverband Biogas
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Biogas producing techniques
Wet fermentation Dry fermentation
Continuous processDiscontinuous/Batch process
Source: Fachverband Biogas
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Biogas producing techniques
Continuous feeding and
removal of small
quantities of substrate
Wet fermentation Dry fermentation
Continuous processDiscontinuous/Batch process
Source: Fachverband Biogas
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Biogas producing techniques
During the digestion the
substrate is neither
added nor removed
from the digester
Wet fermentation Dry fermentation
Continuous processDiscontinuous/Batch process
Source: Fachverband Biogas
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Wet fermentation of Biowaste
Advantages:
Good separation of
organic and impurities
Good substrate digestion
Good suitability for commercial
biowaste
Disadvantages:
× Complex (preparation)
× High energy consumption
× High wear
× Sedimentation
× TS approx. 12% or less
Energy requirement:
Approx. 10% of the plant’s electricity production
Minimum input: approx. 10 000 t/year
Maximum input: approx. 400.000 t/year
Gas production: approx. 100-130 Nm3/tFM
Others: mostly external hygienisationwww.bta-international.de
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Dry fermentation of Biowaste
Advantages:
If modular → only 1 module is
affected in case of process
problems
High loading volume
High solids content: 30-40% TS
Disadvantages:
× Emission during batch loading
× Struvite deposits in the percolate
system
× Lower productivity
Energy requirement:
• Approx. 3-5% of the plant’s electricity production
• Fuel for wheel loaders
Minimum input: approx. 5 000 t/year
Maximum input: approx. 150.000 t/year
Gas production:
approx. 70-100 Nm3/tFM
→ longer operation for more uniform gas quality
Others: necessary hygienisation by composting
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Design parameters for a 1 MW wet digestion plant
• Input
• Expired foodstuff 15.000 Mg/a
• Water 3.450 Mg/a
• Mixed waste 2.000 Mg/a
• Oil and fat 2.850 Mg/a
Total input 23.300 Mg/a
• Output
• Digestion Residue 17.350 Mg/a
• Biogas 3.350 Mg/a
• Packaging and Metals 2.250 Mg/a
Total output 22.950 Mg/a
• Energy
• Electrical energy 6,70 Mio kWh/a
• Thermal energy 7,00 Mio kWh/a
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Exemplary Dates of Biowaste Treatment
Hamburg, Germany
• 07.03.2005: Submission of application
• 01.07.2005: Permit granted for construction
• 15.07.2005: Foundation of BIOWERK Hamburg GmbH & Co. KG
• 10.08.2005: Begin of construction on site
• 17.02.2006: Permit granted for operation
• 15.03.2006: First engine test with Biogas
• 24.04.2006: Official opening of the plant
• 17.07.2006: Start of the operating test
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Operational problems; important issues
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Particle size reduction
Extracting organic material from packaging
Impurities separation
Pretreatment of the feedstock in wet digestion
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Inhomogeneous feedstock problems
• Dishes, cutlery, etc..
• Plastic bags
• Bones, egg and seashells
• Glass, etc..
Issues: mechanisms blocked or broken by material
Solution : separation of impurities
Wet digestion: pre-treatment necessary
Dry batch digestion: less sensitive to impurities → post-treatmentSource: FINSTERWALDER UMWELTTECHNIK
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Feedstock – Removal of impurities from a wet digester
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Biological problems
Issues:
• Ammonia level is high
• Feeding too high or retention time too short (Buffer capacity)
• Lack of trace elements/high sulfur
• Inadequate mixing
• Fast temperature decrease e.g. due to failure in heating systems
• Inhibitors (disinfectant, antibiotics)
Solutions:
• Feedstock as constant as possible
• Periodic check of the biological parameters
• Supplement of trace elements
• Thorough inoculation of input substrates is essential
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Biowaste digestion processes overview in Europe
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Biowaste dry fermentation – Continuous process
Linde KCA/Strabag – process (Germany)• Horizontal concrete digester with several paddle
stirrers in row
• Requires thorough crushing and pretreatment of
organic wastes
• Max 25% DM
DRANCO – process (Belgium)• Vertical cylinder, throughout crushing of organic
wastes
• Mixing with already digested matter (1:6)
• Vertical passage from top to bottom though
cylinder
Kompogas – process (CH), Thöni (AUS)• Horizontal steel or concrete digester with long
axle paddle stirrer
• Requires thorough crushing and pretreatment of
organic waste
• Max 25% DM
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Strabag Umweltanlagen GmbH (formerly Linde-KCA Umweltanlagen GmbH)
The dry digester built as a horizontally arranged, special-concrete, very
sturdy compartment
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Organic Waste System (DRANCO)
• First plant built in 1984
• Vertical digestion: the material drops vertically by gravitational force
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• The volume of each digester is
around 1300 m3
• Retention time in the digester is
about 14-20 days
Axpo Kompogas AG
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Biowaste dry fermentation – Discontinuous process
Simultaneous wet-dry digestion
(agricultural and communal)• Helector and BAL, DE. Renergon, CH
Solid mater immersion process with
flexible cover (agriculture)• Erep, CH. Aria-Biogas, Naskeo, FR.
Wolferstetter, DE
Garage type digester (communal)• Inoculation of substrates and percolation with process
water (Biocell, DK. BEKON, Bioferm, DeNaBa, DE.).
• Additional aerobic pretreatment (Kompoferm, DE.
Solon, DK. Pöttinger, AT)
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Bekon Energy Technologies GmbH & Co.KG
• The standard module has 4 digesters
• Retention time in the digester is about 28-35 days
Source: Bekon Energy Technologies GmbH & Co. KG
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BIOFerm GmbH
• Biggest plant: 8 digesters and a capacity of 750 kWel
• Retention time in the digester is about 4 weeks
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Eggersmann Anlagenbau GmbH & Co. KG
• The standard module has 8 digesters
• Retention time in the digester is about 21 days → pre-process for
composting
Biogas plant Schweinfurt
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Digestate management
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Use of biogas digestate
Digestate can be spread on the fields
• Before the land application the
feedstock/digestate must be
hygienized
• EU animal byproduct regulation, national
biowaste ordinance
Improved Fertilizer
• Avoids nutrient losses
• Reduces burning effect on plants
• Improves flowing properties, plant
compatibility and health
• Reduces germination ability of weed seeds
Environmentally sound
• Reduces the intensity of odor
• 3 folded emission reduction effect avoidance
of methane, laughing gas and ammonia
• Reduces the wash out of nitrate through better fertilizer management
• Recycles organic matter and nutrients
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Upgrading of the digestate
Drying PelletizingLiquid-solid separation
Mineral Organic FertilizerComposting
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Technical and financial success factors
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Technical success factors for biowaste digestion systems
• Substrates need to be suitable for digestion
(stackable, structured, contaminant free)
• Not suitable for the treatment of hazardous wastes
• Thorough inoculation of input substrate is essential
• Active bacteria have to be transported to the substrate (dry
digestion), fresh biomass is transported to the bacteria (wet digestion)
• Digestion process has to support the development of appropriate
bacteria
• Applied technology has to suit local conditions, more than 60 % local
sourcing possible
• Plant size has to be designed according to available quality and quality
of input substrates
• Modular design allows future enlargement of the plant
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Financial success factors for biowaste digestion systems
• Continuous supply of suitable substrate
• Fixed long term waste disposal contracts
• Availability of trained and motivated personnel
• Access to the electricity grid at reasonable rates
• Biowaste disposal fees, e.g. in Europe 20 – 120 €/t
• Revenue from biomethane or electricity sales
• Possibility to utilize excess heat from CHP unit
• Revenue from sales of compost or dried digestate as secondary fuel
• Communal projects are largely not profit driven: payback 15 to 20
years
• But, …. bio-methanisation is the only waste treatment technology with
a positive energy and revenue balance
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Example investment costs
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Example capital costs
Depreciation Years
Building 20
Equipment 10
Gas utilization 8
Mobile machineries 7
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Example operational costs
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Example specific treatment costs
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Thank you for your attention!
Michael Köttner
International Biogas and Bioenergy Centre of Competence IBBK
Am Feuersee 6 • 74592 Kirchberg/ Jagst • Germany
Phone: +49. 7954. 926 203 • Fax: +49. 7954. 926 204
[email protected] • www.ibbk-biogas.com