The Bioenergy System Planners Handbook - BISYPLAN

Originally the project was financed inside the InterReg-programme. The handbook and its spreadsheet aimed to be a fairly complete aid for those planning new, regional, biomass-based energy system solutions.

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- Over-all resources
-- From food residues
-- From society
-- From livestock
-- From landfills
- The EU-market
- The Asian example
Handbook contents

01 Introductions to biomass
01-00 General introduction to biomass
01-01 Ligno-cellulose (wood)
01-02 Herbaceous (crops)
01-03 Putrescible (substrates)
01-04 Others (residues)

02 Resource aspects
02-00 General biomass resources
02-01 Ligno-cellulose resources
02-02 Herbaceous resources
02-03 CURRENT
02-04 Residue resources

03 Supply chains and systems
03-00 General on biomass ageing and supply
03-01 Supply of woody biomass
03-02 Supplying herbaceous biomass
03-03 Supply aspects on putrescible biomass
03-04 Supply of residuals and waste

04 Getting the energy out of the fuel
04-00 General on energy extraction
04-00 contains sections on different processes like combustion, gasification, pyrolysis, upgrading, biochemical treatment etc...
04-01 Process prop. of ligno-cellulose
04-02 Process prop. of herb. biomass
04-03 Process prop. of putrescibles
04-04 Process prop. of residuals

05 Economical aspects and cost structures
05-00 Cost distribution with biomass energy
05-01 Specific costs with of ligno-cellulose
05-02 Specific costs with herbaceous biomass
05-03 Cost structure with putrescibles
05-04 Costs with of residual and waste fuels

02-03: Putrescibles – Resources

It is important to differentiate and carefully to evaluate the theoretical, technical, economical, and realizable potential of biomass or energy.
The theoretical potential comprises all the energy that should theoretically be physically generated within a defined time period and defined space.
The technical potential is specific part of energy of theoretical potential, which can be provided within the given structural and ecological boundaries and by respecting any legal restrictions. It may not always make sense to fully exhaust the technical potential, especially if there is no profitable return.
However, the economic potential may not be realizable without any administrative support from certain institutions.

There is a huge gap between the technical and profitable potential and the realizable potential. A lot of what is technically feasible is rejected for various reasons, mainly special interests, e.g., landscape protection or jobs safety. A lot can be explained rationally but a lot is just based on emotion. The total yield from biomass results from the maximum area available for cultivation and the energetic yield from the biomass cultivated on the specific area.

02-03-01: Over-all resources of digestible (putrescible) biomass (substrates)

According to a study published by the ATEE (Association Technique Energie Environnement) [1], the world’s theoretical potential of biogas would increase 8.72 PWh per year if all waste was treated through anaerobic digestion. If agricultural by-products would be also used for biogas production, the biogas potential would reach 11.6 PWh/year (table 02-03 1). In comparison, world consumption of natural gas is around 2000 PWh per year [2].

World biogas resource Produced biogas (TWh/year) Biogas which can be valued (TWh/year)
Urban and industrial solid waste 8 723 700 - 1 150
Urban and industrial waste water 582 460 to 580
Agricultural by-products 11 630 460 to 1 750
TOTAL 20 934 1 630 to 3 500
Biogas/worldwide
consumption of natural gas
100 % 8 to 17 %
Table 02-03 1: Worldwide resources in according to study of ADEME

Anaerobic micro-organisms can decompose all kinds of organic materials. Of these, short chain hydrocarbons, such as sugars, are easiest to decompose. Longer chain hydrocarbons, such as celluloses and hemicelluloses, are more difficult to decompose and the digestion process will therefore take longer. Woody materials that contain long chain hydrocarbons, such as lignin, are not suitable for decomposition by anaerobic micro-organisms.

The sources of feedstock suitable for AD are many and varied, many billions of tonnes are available worldwide. Within the EU, for example, there are over 1.2 billion tonnes of potential feedstock per annum (Table 2) [2].

Feedstock/Process Produced
Animal manure 1 200
Paper production 2
Sugar beet processing 8
Olive oil production 3
Other fruit and vegetable processing 3
Other food and drink sectors 1
Leather production 0.25
Textile production 0.1
Mineral waste 15
Other sectors 4
Estimated total 1 236
Table 02-03: Estimated quantities of waste recycled to land from main industrial sectors in fifteen member states (million tonnes fresh weight per annum)
(derived from Gendebien et al., 2001)

The data in Table 2 exclude left over and out of date food from supermarkets, households and catering establishments as well as sewage sludge.

02-03-01a: Amounts of digestible from food residues

Figure 02-03 1 illustrates the 2007 production volumes of all commodity groups in their primary form, including animal feed products (which are then factored out using allocation factors).

Commodity production
Figure 02-03 1: Production volumes of different commodities per region (million tonnes), [5]

Roughly one-third of the edible parts of food produced for human consumption gets lost or wasted globally, which is about 1.3 billion ton per year. Food is wasted throughout the food supply chain (FSC), from initial agricultural production down to final household consumption.

In medium- and high-income countries food is to a great extent wasted, meaning that it is thrown away even if it is still suitable for human consumption. Significant food loss and waste do, however, also occur early in the food supply chain. In low-income countries food is mainly lost during the early and middle stages of the food supply chain; much less food is wasted at the consumer level.

Food losses
Figure 02-03 2: Per capita food losses and waste, at consumption and pre-consumptions stages, in different regions [4]

Per capita food wasted by consumers in Europe and North-America is 95-115 kg/year, while this figure in sub-Saharan Africa and South/Southeast Asia is only 6-11 kg/year.

Food losses in industrialized countries are as high as in developing countries, but in developing countries more than 40 % of the food losses occur at post-harvest and processing levels, while in industrialized countries, more than 40 % of the food losses occur at retail and consumer levels.

In the case of cereals (Figure 02-03 3), wheat is the dominant crop supply in medium- and high-income countries, and the consumer phase is the stage with largest losses, between 40-50 % of total cereal food waste.

Cereal losses
Figure 02-03 3: Part of the initial production lost or wasted, at different FSC stages, for cereals in different regions [6]

02-03-01b: Amounts of wastewater sludge from society

Sludge per capita (excluding dredging spoils) was highest in Finland, Austria and Denmark (more than 99 kg per capita) and lowest in Malta, Romania, Germany, Greece and Poland (less than 15 kg per capita) (Eurostat 2008). The percentage of population connected to wastewater collection and treatment systems varies from 29-30% in Romania and Cyprus to 90-99% in the Austria, Germany, Spain, Switzerland and Netherlands (mixed reference years).

More than two thirds of the sludge was used as fertiliser in agriculture in Cyprus, Spain, Ireland and the United Kingdom, while another five Member States (Lithuania, Bulgaria, Luxembourg, France and Latvia), as well as Norway, reported between one and two thirds of their total mass of sewage sludge being disposed of through agricultural uses.

In contrast, more than two thirds of sewage sludge was composted in Estonia, Finland and Slovakia.

Atlantic Boreal Continental Mediterranean
Belgium 863 242 Estonia 72 383 Austria 847 453 Bulgaira 1 182 360
Denmark 541 749 Finland 818 011 Czech Rep. 1 239 164 Cyprus 7 019
France 2 317 490 Latviva 95 593 Germany 2 033 096 Greece 161 732
Iceland Lithuanina 57 038 Hungary 223 711 Italy 1 223 235
Ireland 154 242 Norway 101 398 Poland 401 277 Malta 173
Luxembourg 14 024 Sweden 669 486 Romania 216 883 Spain 1 945 536
Netherlands 26 870 584 Slovakia 1 164 067
Portugal 792 182 Slovenia 607 186
UK 19 888 143 Switzerland
Table 02-03 3: Common sludge in 2008 including dredging spoils, tons [4]


Atlantic Boreal Continental Mediterranean
Belgium 600 Estonia 6 356 Austria 1 574 Bulgaira 73
Denmark Finland 605 Czech Rep. 2 277 Cyprus 35
France 17 080 Latviva 673 Germany 9 933 Greece 206
Iceland 18 Lithuanina 543 Hungary 593 Italy
Ireland 431 Norway 2 198 Poland 3 153 Malta 3
Luxembourg 270 Sweden 1 298 Romania 281 Spain 1 819
Netherlands 356 Slovakia 500
Portugal 3 900 Slovenia 267
UK 8 047 Switzerland 890
Table 02-03 4: Number of urban waste water treatment plants (mixed years 2006-2009) [5]

02-03-01c: Amounts of digestible biomass from livestock

One of the largest raw material potential for biogas production comes from manure from animal (cattle, pigs, sheep, goats and horses) and poultry breeding (hens and broilers).

Animal and poultry breeding biodegradable residues are several types of manure. Manure can be classified according to the dry matter content. Type of produced manure depends on the animal type and size of the company. One of the most suitable raw materials for production of biogas is manure from animal farms. The following tables (5, 6 and 7) consist numbers of livestock in chosen countries.

Atlantic Boreal Continental Mediterranean
Belgium 2 600 450 Estonia 237 900 Austria 1 997 210 Bulgaira 564 904
Denmark 1 540 340 Finland 918 268 Czech Rep. 1 349 290 Cyprus 55 589
France 19 199 300 Latviva 380 200 Germany 12 944 900 Greece 620 000
Iceland 73 498 Lithuanina 770 900 Hungary 701 000 Italy 6 446 700
Ireland 6 716 100 Norway 877 711 Poland 5 700 020 Malta 17 777
Luxembourg 196 470 Sweden 1 538 280 Romania 2 684 000 Spain 6 020 200
Netherlands 3 996 000 Slovakia 483 810
Portugal 1 438 700 Slovenia 469 983
UK 9 901 000 Switzerland 1 597 480
Table 02-03 5: Number (head) of cattle in chosen countries, 2009 [6]


Atlantic Boreal Continental Mediterranean
Belgium 6 321 060 Estonia 364 900 Austria 3 064 230 Bulgaira 783 649
Denmark 12 369 100 Finland 1 381 210 Czech Rep. 1 909 230 Cyprus 464 932
France 14 810 000 Latviva 383 700 Germany 26 886 500 Greece 942 000
Iceland 43 286 Lithuanina 897 100 Hungary 3 383 000 Italy 9 252 400
Ireland 1 468 200 Norway 839 346 Poland 14 278 600 Malta 65 511
Luxembourg 80 217 Sweden 1 528 740 Romania 6 174 000 Spain 26 289 600
Netherlands 12 108 000 Slovakia 740 862
Portugal 12 339 Slovenia 432 011
UK 4 601 000 Switzerland 1 557 200
Table 02-03 6: Number (head) of pigs in chosen countries, 2009 [6]


Atlantic Boreal Continental Mediterranean
Belgium 33 240 Estonia 1 757 Austria 14 500 Bulgaira 15 765
Denmark 19 224 Finland 4 918 Czech Rep. 24 042 Cyprus 3 010
France 122 364 Latviva 3 920 Germany 118 000 Greece 31 800
Iceland 261 Lithuanina 8 841 Hungary 31 165 Italy 120 000
Ireland 13 500 Norway 3 879 Poland 124 129 Malta 500
Luxembourg 97 Sweden 7 159 Romania 84 373 Spain 138 000
Netherlands 96 862 Slovakia 13 259
Portugal 39 000 Slovenia 2 393
UK 159 288 Switzerland 8 741
Table 02-03 7: Number (1000 heads) of chickens in chosen countries, 2009 [6]

The gas yield (productivity) and content of volatile solids from agricultural biogas installations depends on the composition of the substrate, the technologies and conversion facilities.

Mean production
m3/tFM [10]
Mean methane content
% by volume
Liquid manure from calves: 23 55.7
Liquid manure from fatling herd: 22 56.3
Liquid manure from dairy herd: 20 61.9
Solid manure from cattle: 21 57.1
Solid manure from pig: 15 60.8
Manure from cattle: 60 53.2
Manure from poultry: 231 51.4
Table 02-03 8:Average data for biogas yield from different livestock [7]

The total animal waste per capita is the highest in Ireland, Austria, Belgium, Estonia and Poland (more than 40 kg per person) and lowest in Bulgaria, Romania, Italy and Germany and Greece (less than 5 kg per person), see at the Table 9.

Atlantic Boreal Continental Mediterranean
Belgium 498 265 Estonia 5 983 Austria 4 337 Bulgaira 9 624
Denmark 165 966 Finland 15 246 Czech Rep. 66 112 Cyprus 20 583
France 1 593 570 Latviva 35 985 Germany 333 343 Greece 40 414
Iceland Lithuanina 85 761 Hungary 230 927 Italy 93 455
Ireland 228 122 Norway 675 654 Poland 1 583 196 Malta 8 857
Luxembourg 2 263 Sweden 145 015 Romania 48 916 Spain 1 626 994
Netherlands 506 935 Slovakia 43 136
Portugal 139 034 Slovenia 33 292
UK 2 526 278 Switzerland
Table 02-03 9: Animal waste of food preparation and products, 2008 (tonnes) [5]

02-03-01b: Amounts of digestible from landfilling

In the EU27, 513 kg of municipal waste was generated per person in 2009. The amount generated per person varied from 316 kg in the Czech Republic and Poland to 833 kg in Denmark.

On average in the EU27, 504 kg of municipal waste was treated per person in 2009. Municipal waste was treated in different ways: 38 % was landfilled, 20% incinerated, 24 % recycled and 18 % composted. (Eurostat news release 2011). The highest shares of incinerated municipal waste were observed in Sweden (49 % of waste treated), Denmark (48 %), the Netherlands (39 %), Luxembourg (36 %), Belgium (35 %), Germany and France (with 34 %).

In ten Member States incineration was equal to or below 1%. Also refer to section 02-04-01.

Atlantic Boreal Continental Mediterranean
Belgium 159 Estonia 287 Austria 34 Bulgaira 3 421
Denmark 130 Finland 1 180 Czech Rep. e 2 114 Cyprus e 540
France 10 802 Latviva 694 Germany 176 Greece 4 181
Iceland s 121 Lithuanina 1 093 Hungary 3 212 Italy 15 488
Ireland 1 724 Norway 324 Poland 7 859 Malta 255
Luxembourg 61 Sweden 63 Romania 6 164 Spain 14 540
Netherlands 65 Slovakia 1 411
Portugal 3 342 Slovenia 628
UK 16 020 Switzerland 0
Table 02-03 10: Deposit of municipal waste onto or into land in 2009, thousands of tonnes [5]
Comments: e - estimated, p -provisional value, s - Eurostat estimate

The total amount of waste deposited into landfills per capita is smallest in Switzerland, Germany, Austria, Netherlands, Sweden and Belgium (below 20 kg/person) and highest in Malta, Cyprus, Bulgaria, Ireland, Iceland and Greece (over 350 kg/person).

02-03-02: Market development in EU [8]

Biogas production rose across the EU in 2009, driven by the EU target of meeting 20 % of final energy consumption with renewable energies and the guidelines set forth in EU Directive 2008/98/EC for the handling of waste. On the basis of these political objectives, many countries have introduced incentive programmes for the generation of power from biogas (feed-in tariffs for electricity from biogas, green certificates, tenders or grants for the use of energy crops).

Power generation from biogas grew between 2008 and 2009 by almost 18 % and accounted for a total of 25 170 gigawatt hours (GWh) in 2009.

Total energy extraction from biogas rose over the same period by some 4.3 % to just above 97 TWh.

Around 52 % of the plants produced biogas from agricultural waste, while landfills and sewage treatment plants generated 36 %, or 12 % of the biogas in the EU. In 2009, the largest biogas producers in Europe (in thousands of tonnes of oil equivalent or ktoe) were Germany, the United Kingdom, France, Italy and the Netherlands. Rapid and dynamic growth can be observed in Greece, Slovenia, Slovakia, the Czech Republic and Belgium.

Prim. energy from biogas
Figure 02-03 4: Primary energy production from biogas per capita in the EU in 2009 (MWh/1000 inhabitants)

Data for primary energy production in the EU from landfill gas, sludge gas and other biogas is given in following tables (Table 02-03 11 and Figure 02-03 4).

2008 2009 - Estimated numbers
State Landfill gas Sew. sludge gas1 Other biogas2 TOTAL
2008
Landfill gas Sew. sludge gas1 Other biogas2 TOTAL
2009
Germany 3 392 4 474 41 323 49 189 3 088 4 497 41 417 49 002
UK 16 479 2 426 0 18 903 17 147 2 902 0 20 049
France3 4 411 529 329 5 270 5 144 526 450 6 120
Italy 3 952 35 782 4 768 4 208 58 901 5 167
Netherlands 516 568 1 541 2 625 456 569 2 091 3 116
Spain 1 826 229 309 2 363 1 639 116 383 2 136
Austria 56 255 1 719 2 029 57 220 1 642 1 920
Czech Republic 342 392 314 1 047 340 392 779 1 511
Belgium 543 17 458 1 019 515 24 909 1 450
Sweden 383 655 155 1 191 401 698 171 1 270
Denmark 74 235 782 1 091 72 233 854 1 158
Poland 398 691 30 1 118 413 675 52 1 140
Greece 329 59 2 391 538 142 2 683
Finland 397 127 0 523 356 124 0 481
Ireland 301 94 16 412 274 94 48 416
Hungary 24 93 136 254 33 120 204 357
Portugal 0 0 267 267 0 0 277 277
Slovenia 95 36 31 164 97 35 128 261
Slovakia 2 110 7 120 9 172 8 190
Luxembourg 0 0 107 107 0 0 143 143
Latvia 77 26 0 102 81 31 0 113
Lithuania 5 20 10 35 15 24 14 55
Estonia 23 10 0 33 23 10 0 33
Romania 0 0 7 7 1 8 6 15
Cyprus 0 0 2 2 0 0 2 2
EU Total 33 623 11 081 48 326 93 032 34 909 11 673 50 482 97 180
Table 02-03 12:Primary biogas energy output in the EU 2008 and 2009 (ktoe) [3]
                    To obtain TWh from ktoe, divide by 85.985
                    1 Urban and industrial
                    2 Decentralised agricultural plants, municipal solid waste methanisation plants and centralised co-digestion plants
                    3 French overseas departments excluded


02-03-02a: Example: Biogas development in Asia

Production of biogas via anaerobic digestion is a relatively simple carbon-reducing technology that can be implemented at commercial, village and household scales. It allows for the controlled management of large amounts of animal dung and the safe production of gas for cooking, lighting or power generation.

In addition, as a by-product, it provides a valuable agricultural fertilizer.

Worldwide 25 million households obtain their energy for lighting and cooking from biogas, including 20 million households in China and 3.9 million in India.

In China, biogas is heavily promoted by the government by providing subsidies for biogas digesters. Some analysts estimate that more than 1 million biogas digesters are now being produced each year in China. Beyond the household scale, several thousand medium- and large-scale industrial biogas plants are installed at China livestock and poultry farms. This number is expected to increase following a recent national biogas action plan, under which the government aims to have 50 million rural people using biogas as their main fuel in 2010 and 300 million in 2020.

In Nepal, Vietnam, Cambodia, Laos and Bangladesh, with support from the SNV/Biogas Support Programme, more than 244 000 household biogas installations were installed between 2004 and 2008. This has benefited 1.6 million people by reducing household expenses and workload on fuelwood collection, by improving indoor health conditions and by producing high-quality organic fertilizers. In addition, reduced demand for fuelwood has a positive impact on the environment.

Dissemination of the digesters was made possible by the development of a tried and tested technology combined with a successful implementation strategy involving households, government services, non-governmental organisations, the private sector and external financing.


References

1 Biogas renewable energy.
2 BP Statistical Review of World Energy. June 2011.
3 Lukehurst CT, Frost P, Seadi TA. Utilisation of digestate from biogas plants as biofertiliser. IEA Bioenergy, 2010.
4 Gustavsson J, Cederberg C, Sonesson U. Global food losses and food waste. Swedish Institute for Food and Biotechnology (SIK). Gothenburg, Sweden. FAO 2011.
5 Eurostat.
6 Food and Agriculture Organization (FAO) of the United Nations.
Download the report "Food losses and Food waste"
7 Põllumajanduses kasutatavate biogaasiseadmete gaasitootlus. Mecklenburger Biogas Gesellschaft MbH, KTBL
8 Biogas market development. German Energy Agency.
9 The EurObserv'ER site publishes regular reports on different aspects of renewable energy development