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 |
(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).
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.
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.
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.
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