Next Article in Journal
Economic and Social Aspects of Using Energy from PV and Solar Installations in Farmers’ Households in the Podkarpackie Region
Next Article in Special Issue
Mitigating the Energy Consumption and the Carbon Emission in the Building Structures by Optimization of the Construction Processes
Previous Article in Journal
A Data Driven RUL Estimation Framework of Electric Motor Using Deep Electrical Feature Learning from Current Harmonics and Apparent Power
 
 
Search for Articles:
Title / Keyword
Author / Affiliation / Email
Journal
Article Type
 
 
Advanced Search
 
Section
Special Issue
Volume
Issue
Number
Page
 
Journals
Energies
Volume 14
Issue 11
10.3390/en14113157
energies-logo
Submit to this Journal Review for this Journal Propose a Special Issue
► Article Menu

Article Menu

share Share announcement Help format_quote Cite question_answer Discuss in SciProfiles thumb_up
...
Endorse textsms
...
Comment
first_page
settings
Order Article Reprints
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

The Efficiency of the Biogas Plant Operation Depending on the Substrate Used

by
Janina Piekutin
1,
Monika Puchlik
2,*,
Michał Haczykowski
3 and
Katarzyna Dyczewska
2
1
Department of Technology in Environmental Engineering, Faculty of Construction and Environmental Sciences, Bialystok University of Technology, 45A Wiejska Str., 15-351 Bialystok, Poland
2
Department of Forest Environment, Faculty of Construction and Environmental Sciences, Bialystok University of Technology, 45A Wiejska Str., 15-351 Bialystok, Poland
3
White Moose, 13A K. Szałasa Str., 03-180 Warsaw, Poland
*
Author to whom correspondence should be addressed.
Energies 2021, 14(11), 3157; https://doi.org/10.3390/en14113157
Submission received: 9 May 2021 / Revised: 25 May 2021 / Accepted: 25 May 2021 / Published: 28 May 2021
(This article belongs to the Special Issue Innovations-Sustainability-Modernity-Openness in Energy Research 2021)
Browse Figures
Versions Notes

Abstract

:
The study aimed to assess the most efficient solution of raw material management in selected biogas plants into the concept of circular economy and evaluate the most efficient solution of raw material management in selected biogas plants due to the quality and quantity of the feed and the final product obtained, which is biogas, as well at the closed circulation (circular economy). The study evaluated two agricultural biogas plants on a real scale and one at the sewage treatment plant (in real scale) in northeastern Poland. A year-long study showed that in technical terms, the best work efficiency is achieved by agricultural biogas plants processing: silage, manure, apple pomace, potato pulp (biogas plant No. 1), followed by biogas plant No. 3 processing chicken manure, decoction, cattle manure, poultry slaughterhouse waste (sewage sludge, flotate, feathers), and finally, the lowest efficiency biogas plant was No. 2, the sewage treatment plant, which stabilized sewage sludge in the methane fermentation process. Moreover, based on the results, it was found that agricultural biogas gives the best efficiency in energy production from 1 ton of feed.

1. Introduction

Energy is the lifeblood of modern civilization. Biogas is a viable source of energy to tackle the problem of this energy crisis in agriculture-based developing countries [1]. The increasing use of biogas, produced from energy crops, is supposed to change agricultural landscapes in Europe [2]. Protecting the environment from these harms and reducing these adverse effects has become the most crucial target of many countries globally [3,4]. The solutions can be found via renewable energy sources by producing “green power”. Currently, the world level of technical development of biogas plants is very diverse. Several million simple installations in Asia are built using economical methods of digging uninsulated fermentation chambers [5]. The study′s primary objective in Northern Germany was to quantify the assumed impact of intensive biogas production with the example of an agricultural landscape [2]. It is a cheap, straightforward, and at the same time, very effective way of processing waste [6].
In Europe, the primary biogas producers are Finland [7], Austria, Denmark, and Germany [2,8]. On the old continent, biogas production varies significantly between countries due to the level of development. In 2013–2017, the use of agricultural biogas increased significantly, while biogas from sewage treatment plants, such as landfill biogas in 2015 and 2016, had their best time, which is associated with a slowdown in the development of these installations in favor of agriculture [5,6,8]. The inhibition of these industries is probably caused by the modernization of wastewater treatment and production of less sludge and the growing awareness of residents about sorting and reducing waste production.
As of 31 December 2017, there were 310 biogas plants in Poland, of which 96 were installations producing agricultural biogas and 214 were other biogas plants. In the group of biogas plants, the remaining 50.47% are biogas plants at sewage treatment plants, 47.62% are biogas plants at landfills, and 1.91% are mixed biogas plants [9]. The material used in biogas production from sewage treatment plants is excessive activated sludge precipitated from municipal and industrial sewage. Installations for the production of agricultural biogas use biomass from unique farms growing high-energy plants, by-products of processing, and plant and animal waste. Until 2015, about 1200 farms dealing with cattle breeding, 3000 farms dealing with pig breeding, and 3500 farms dealing with poultry were registered in Poland—a total of 7800 farms with livestock density above 100 LU, where biogas production is possible, technically justified, and economical [10]. It results, among others, from this branch structure in Poland that is characterized by a great degree of fragmentation [11].
The proper management of livestock manure has a much greater potential to reduce methane emissions, especially in cattle manure [4,12,13,14]. It should be emphasized that manure stored in piles is a source of essential methane emissions, the scale of which may reach tens of thousands of tons per year in Poland [15]. Almost 59% of the world′s methane emissions are of anthropogenic origin, of which the largest share (40–53%) is agriculture, especially intensive production [5]. In the EU, the percentage of agriculture in anthropogenic methane emissions is 53%, 26% is methane from waste, and 19% comes from energy production [4,6].
As these types of solutions increase, the ratio of greenhouse gas emitted in the atmosphere decreases, which is an exceptionally environmentally friendly approach [3]. Additionally, the production of biogas in agricultural areas may provide additional income from agricultural activities, which can develop the local economy in rural areas and promote circular economy principles in local communities [15,16,17]. Biogas is considered a renewable energy source [10,18]. Therefore, its production allows the increase of the share of these sources in the national energy mix, which is the EU′s goal as set out in the renewable energy directive (RED II) [4,19].
The choice of production technology depends on the type of substrates processed, dry matter content in the fermentation chamber 2–6, number of process stages, and temperature at which the fermentation is carried out.
The paper presents the most efficient composition of a raw materials mixture used in two agricultural biogas plants and one based on sewage sludge. Attention was paid to the possibilities of individual substrates to obtain good quality methane in large quantities. In addition, the environmental aspect of wastewater treatment and agricultural waste disposal has been taken into account. The study aimed to assess the most efficient solution of raw material management in selected biogas plants due to the quality and quantity of feedstock and the final product obtained, which is biogas and the closed circulation (circular economy) [8].

2. Materials and Methods

Three biogas plants in real scale were selected for the research: two agricultural and one based on sewage sludge. A local visit was carried out in each of them, and data related to the type, amount of feed obtained, and technology used were collected. Data collection was carried out throughout 2018 in agricultural biogas plant No. 1, with a capacity of 1 MW. The biogas plant uses technology with the flow of biomass to two digesters with a capacity of 4241 m3 each and the third for storage of digestate with a capacity of 6.433 m3 [8]. In the event of a failure, excess biogas is burned in a flare with a throughput of 600 m3/h. The planned capacity of the biogas plant is 1 MW of electricity generation and 941 kW of thermal energy generation. According to Ahmad et al., the energy is the lifeblood of modern civilization. Biogas is a viable source of energy to tackle the problem of this energy crisis in agriculture-based developing countries [1]. The quantitative composition of administered solid substrates in 2018 divided into months is presented in Table 1.
Biogas plant No. 2 (Figure 1c,d) is built in the sewage treatment plant to stabilize the sewage sludge in the methane fermentation process. Sludge is continuously pumped into the tank to four separate fermentation chambers with a capacity of 7700 m3 each. Biogas is stored in a flexible, low-pressure two-shell gas tank with a capacity of 5000 m3.
Agricultural biogas plant No. 3 (Figure 1a,b) processes only agricultural production waste, such as chicken manure in the amount of 18,250 t/year, gravel decoction in the amount of 5000 t/year, cattle manure in the amount of 30,000 t/year, and waste from poultry slaughterhouses (sewage sludge, flotation mass, feathers) in the amount of 10,950 t/year. All waste is collected in the 300 m3 primary tank. The purified biogas is directed to a co-generation system, which is known as the combined energy management system, or a combined heat and power system with 1 MW electric and 1.05 MW heat power. In the summer of 2018, the biogas plant took up the most liquid manure, similar amounts of chicken manure and slaughterhouse flotation mass, twice as few flotation mass from dairy and whey from cheese production, and small amounts of plant weight and stomach contents of animals. In the autumn of 2018, chicken manure constituted the most, there was slightly less bovine manure, and flotation mass also played a significant role with whey and dairy flotation mass added to this mix of substrates. The slurry is used to a large extent in winter and spring. Chicken manure is delivered in similar quantities monthly. During the year, agricultural biogas plant No. 3 processed 35,254.97 tons of raw materials. Agricultural biogas plants are becoming attractive in several countries, mainly due to the possibility of obtaining additional incomes by selling energy to the electrical grid [19].

Theoretical Background

The formulas No. 1 and No. 2 were used to calculate the unit biogas production and fermentation efficiency.
Unit biogas production (JPB) is the volume of dry biogas or methane produced per unit time per unit mass of the input substrate. The amount of gas obtained from kg d.m.o. is described by the formula:
J P G = G / Ł D
where JPG—(m3/kg d.m.o.); G—daily biogas production, (m3/d); ŁD—daily load, (kg/d).
Fermentation efficiency (degree of conversion) (Ge) is the only indicator that allows comparing the efficiency of different systems, which is defined as the quotient of the daily production of biogas in installations and the daily production of biogas determined under optimal conditions for the same waste (in laboratory conditions at 100% efficiency processing (Gmax)):
G e = G / G m a x · 100 ( % )
where Ge—fermentation efficiency, (%); G—daily biogas production in installations, (m3/d); Gmax—daily biogas production determined under optimal conditions for the same waste (in laboratory conditions with 100% processing efficiency), (m3/d).

3. Results and Discussion

Evaluation of the work of selected biogas plants with the raw materials used.
Three different biogas plants have been assessed. Two of them were agricultural biogas plants and the third was the biogas plant at the sewage treatment plant. All these biogas plants carry out wet fermentation but in different conditions. In biogas plant No. 1, biogas is produced in two main fermentation tanks, and in the third, digestate, additional methane that did not manage to release, is recovered. In biogas plant No. 3, the digestate container is open, and no biogas residues are recovered. In biogas plant No. 2, the digested sludge goes to open averaging and degassing tanks, from where it is fed to compaction and dried to a granular fertilizer. Table 2 presents the most essential components and differences in the construction of a biogas plant. All three biogas plants operate in continuous filling mode.
Biogas plants operate using different substrates with higher or lower efficiency (Figure 2). Biogas plant No. 2 processes an average of 47 m3 of sludge per day, which is kept for 40 days. Sixty-two tons of substrates are processed daily at biogas plant No. 1. Biogas plant No. 3 processes around 98 tons of waste per day, which is held for 22 days. The type of raw materials used is not accidental and has an economic basis [7,8,9].
In the winter months (Figure 2), due to the low air temperature, energy demand did not decrease, and more feedstock was processed in agricultural biogas plants. The opposite (Figure 2) is the situation with biogas plant No. 2, which is mainly used to treat sewage sludge. A sudden increase in the amount of sludge may have resulted from a reduced efficiency of wastewater treatment. The non-concentrated sludge went to digesters with high hydration (>97%), thus inhibiting the amount of biogas produced. For the biogas production from feedstock (Figure 3), the highest amounts are obtained in biogas plant No. 1, which consumes the least raw materials and produces the most biogas [20,21,22].
In 2018 (Figure 3), biogas plant No. 1 produced on average 117 m3 of biogas from 1 ton of substrates. The most effective production efficiency in May and June was from 123 to 127 m3/t, and it was the lowest in April, September, and November: from 105 to 106 m3/t. The only exception was June (127), in which production was recorded for unexplained reasons. This might be due to the supply of large amounts of manure and potato pulp in the previous month, which supplied much biogas only after some retention time. Agricultural biogas plant No. 3 produces slightly less biogas from its substrates. Due to the quarterly data obtained, the monthly amounts presented are averaged. In the third quarter of 2018, the biogas plant monthly produced an average of 85.4 m3 of biogas from one ton of substrates; in the fourth quarter, this value jumped to 96.2 m3/t; in the first quarter of 2019, production was 73.2 m3/t, and in the second quarter, it was 76.8 m3/t. In Figure 4, winter months were compared with other winter months and summer months with additional summer months. The summary of data from 2019 and later from 2018 illustrates the situation throughout the year.
In terms of the production of cubic meters of biogas from 1 cubic meter of sludge, the weakest results were obtained in biogas plant No. 2 (Figure 4). Due to high hydration, large volumes of sludge are used for production, and production efficiency is somewhat artificially low. The reactors contain about 3% of dry matter, and in agricultural biogas plants, this amount is much higher. The amount of biogas produced from a cubic meter of sludge from January to June was an average of 27 m3/month; in July, a much more considerable amount of sludge was fermented. The rate dropped to 15 m3/month; from August to December, the amount of biogas was at a similar level of 20 m3/month. Probably, the sludge might not be sufficiently drained, and its volume increased, while production decreased [23,24,25]. By converting the obtained biogas to the amount of dry mass in the sludge, the situation would become reversed entirely from which it arose. The biogas generated at the sewage treatment plant would be a leader in the production efficiency, with the results from January to June on average 930 m3/m3 DM/month, July 496 m3/m3 DM/month, and from August, 721 m3/m3 DM/month on average. It should be emphasized that such biogas yield efficiency in agricultural biogas plants cannot be achieved.
Most heat energy (Figure 5) was produced during the heating season (September 1 to May 31 insofar as weather conditions require a continuous supply of heat to heat buildings) [10]. Biogas plant No. 2 (Figure 3) produces more heat than biogas plant No. 1 (agricultural production waste) because of the size of the plant and the technology used. Biogas plant No. 2 at the sewage treatment plant generated the most significant amount of electricity and heat [26]. Biogas plant No. 3 (agricultural production waste, with technical facilities of 1 MW electric power and 1.05 MW thermal power) comes second in terms of electric energy produced. The biogas plant provides electricity and heat supply to the neighboring plant; therefore, it must work very efficiently throughout the year. The least produced biogas was shown by plant No. 1, which did not produce 100% of its power all year round because of its generator failures. This biogas plant consumes a small amount of available energy for its needs; hence, it can afford small decreases in energy produced [27,28,29,30]. In Turkey, there are detailed systems in an industrial biogas plant; thus, as an alternative method to the classical energy productions, the concept that energy can be consumed where it is produced has been successfully applied today to minimize the increase energy costs and use more efficient and clean energy [3].
It was found (Figure 6) that for the production of 1MW of energy, the most feedstock was used in biogas plant No. 2, an average of 22.56 m3 of sludge; to improve biogas yield from one m3, it would be necessary to reduce the sludge hydration. Given that biogas produced at the sewage treatment plant is during sludge disposal, there is no reason to increase the sludge thickening before fermentation and increase production efficiency [23,24]. As an excellent alternative choice, biogas production by evaluating organic wastes in an industrial biogas plant, methane gas is produced and converted into heat and electricity energy in co-generation systems [3]. Biogas plant No. 3 needs an average of 4.7 tons of charge to produce 1 MW of power, while biogas plant No. 1 needs only 3.37 tons. Considering the amount of feedstock to produce 1 MW of energy in a biogas plants, the input used has more methane and is more caloric than the input used in biogas plant No. 3. The efficiency and reliability of the devices used significantly impact the final effect of obtaining the biogas for production. The higher the reliability, the higher the efficiency [31,32,33,34,35].
When comparing agricultural biogas plants and sewage treatment plants, the purpose of their operation should be kept in mind [36,37]. The best feedstock working in an agricultural biogas plant will not meet the expected goal in a biogas plant and vice versa. First of all, agricultural biogas produced from corn silage, manure, slurry, fruit pomace, mulch, stomach contents, and potato pulp give the best energy production efficiency from 1 ton. If you want to create profitable production, you must produce most of the annual demand for substrates yourself or import them at very bargain prices. The size of a biogas plant has a considerable impact on production. It can be seen in the example of biogas plant No. 3, which has the minor biogas facility producing an average amount of biogas, consuming a moderate amount of substrates, and having an average efficiency of biogas production compared to other biogas plants. Still, it processes vast amounts of waste (35 255 t/year) at the expense of a short holding time of substrates. It is possible to increase biogas production from the feedstock, which is liquid manure, chicken manure, slaughterhouse, and dairy flotation mass, poultry feathers, cheese whey, plant mass, and stomach contents [26,38,39]. An additional sealed digestate tank should be built to recover biogas and modify batch hold time.
Biogas plant No. 1 is characterized by the highest efficiency coefficient of biogas production, with the lowest biogas production and consumption of substrates. Low demand for products also translates into lower maintenance costs, i.e., higher earnings. This biogas plant fits best with its technology and the substrates used for biogas production in terms of price and output. In addition to financial aspects, it is necessary to pay tangible ecological and legal benefits for building the biogas plants [14,15,17]. Due to this, it cares for the environment without using non-renewable natural resources and eliminating the effects of global warming [10].
Biogas plant No. 2 at the sewage treatment plant has a different purpose than a typical agricultural biogas plant. Biogas can be used to produce and reduce the operating costs of the treatment plant. Substrates for biogas production are waste from other processes at the treatment plant. No costs are incurred, which translates into potential profit. The biogas produced is valuable waste from sludge disposal and is of outstanding quality. Since substrates are obtained for free while protecting flora and fauna against harmful effects of wastewater, biogas plants at sewage treatment plants are the best solution for biogas production [40]. Biogas production in wastewater treatment plants (WWIPs) plays a decisive role in reducing CO2 emissions and energy needs in the context of the water–energy nexus [41,42,43,44,45].
In technical terms, the best work efficiency is achieved by biogas plant No. 1, followed by biogas plant No. 3, and finally biogas plant No. 2. Given that biogas installations are designed to do more than just economic profit, namely environmental protection, and natural resources, biogas plants at sewage treatment plants are the unquestioned leader in this respect. They produce suitable quality biogas during waste disposal, which is perfectly suited to turning it into energy reused [46,47,48,49,50]. As Kowalczyk-Juśko et al. showed for the biogas production in Poland, there is a lot of interest in constructing installations of various scales [51].

4. Conclusions

Considering that the input used is one of the most critical factors determining the amount and energy value of biogas, there is still no information on the efficiency of energy production from agricultural waste and sewage sludge, especially when designing biogas plants. Comparing the production efficiency of various methods of obtaining energy from biogas enables the detection of factors that make the processes carried out more efficiently. When preparing models of financial and economic analysis of projects for the construction of agricultural biogas plants, both those that are smaller (up to 0.5 MW) and more prominent, researchers should pay attention to the “energy quality” of the substrates, whose chemical energy in the fermentation process in the final stage is used to power the co-generation system into the environment. It means that the values of the dry matter content of the substrates and the dry organic matter content of the dry matter can significantly influence the efficiency already in the early planning of a biogas plant project. Therefore, it is vital at the initial stage of the project to perform a substrate efficiency test, and on this basis, specific technological solutions of a biogas plant should be adopted, which is necessary for the performance of an energy balance allowing, as a result, estimation of the amount of produced electricity and heat. The data presented in the article show that the tested biogas plants did not analyze the energy content of the raw material but focused on the ease of obtaining the raw material, which in turn translated into benefits in the form of reducing greenhouse gas emissions to the environment and improving energy security. Moreover, the analyzed agricultural biogas plants will stimulate the development of local entrepreneurship and activate the countryside economically by creating new jobs. The use of the produced biogas leads to a reduction in purchased energy consumption and waste disposal in a biogas plant based on a sewage sludge treatment system at a sewage treatment plant.

Author Contributions

J.P. performed the experiment conceived. J.P., M.P., M.H., and K.D. performed the experiment conceived and analyzed the data and then wrote the paper. All authors have read and agreed to the published version of the manuscript.

Funding

Studies was carried out within the framework: WZ/WB-INL/3/2021 and WZ/WB-IIS/2/2021 and financed from the science funds for Ministry of Science and Higher Education.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Data sharing is not applicable to this article.

Acknowledgments

Studies was carried out within the framework: WZ/WB-INL/3/2021 and WZ/WB-IIS/2/2021 and financed from the science funds for Ministry of Science and Higher Education.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Ahmad, S.; Razzaq, S.; Rehan, M.A.; Hashmi, M.A.; Ali, S.; Amjad, M.S.; Mehmood, U. Experimental Investigation of Novel Fixed Dome Type Biogas Plant using Gas Recovery Chamber in Rural Areas of Pakistan. Int. J. Renew. Energy Res. 2019, 9, 1537–1547. [Google Scholar]
  2. Csikos, N.; Schwanebeck, M.; Kuhwald, M.; Szilassi, P.; Duttmann, R. Density of Biogas Power Plants as An Indicator of Bioenergy Generat-ed Transformation of Agricultural Landscapes. Sustainability 2019, 9, 11. [Google Scholar]
  3. Kilic, M.K.; Abut, N.; Kilic, F.C.; Eyidoğan, M.; Kaya, D. An examination of measuring and control systems in an industrial biogas plant in turkey. Int. J. Ecosyst. Ecol. Sci. (IJEES) 2019, 9, 11–16. [Google Scholar] [CrossRef]
  4. Pochwatka, P.; Kowalczyk-Juśko, A.; Sołowiej, P.; Wawrzyniak, A.; Dach, J. Biogas Plant Exploitation in a Mid-dle-Sized Dairy Farm in Poland: Energetic and Economic Aspects. Energies 2020, 13, 6058. [Google Scholar] [CrossRef]
  5. Yu, Q.; Li, H.; Deng, Z.; Liao, X.; Liu, X.; Liu, J. Comparative assessment on two full-scale food waste treatment plants with different anaer-obic digestion processes. J. Clean. Prod. 2020, 263, 121625. [Google Scholar] [CrossRef]
  6. Jarrar, L.; Ayadi, O.; Al, A.J. Techno-economic Aspects of Electricity Generation from a Farm Based Biogas Plant. J. Sustain. Dev. Energy Water Environ. Syst. 2020, 8, 476–492. [Google Scholar] [CrossRef] [Green Version]
  7. Ervasti, S.; Vainio, M.; Tampio, E. Use of local resources as co-substrates in a farm-scale biogas plant. Open Agric. 2019, 4, 650–660. [Google Scholar] [CrossRef]
  8. Perez, V.; Mota, C.R.; Munoz, R.; Lebrero, R. Polyhydroxyalkanoates (PHA) production from biogas in waste treatment facilities: Assessing the potential impacts on economy, environment and society. Chemosphere 2020, 255, 126929. [Google Scholar] [CrossRef]
  9. Nikiciuk, M. Ecological and progrowth potential of agricultural biogas sector in podlaskie voivodeship. Pol. To-Warzystwo Ekon. 2018, 3, 98–117. [Google Scholar]
  10. Załuska, M.; Piekutin, J.; Magrel, L. Economic and energetic efficiency of biogas plant depending on the substrate appli-cable. Oficyna Wydawnicza Politech. Białostockiej 2018, 9, 51–56. [Google Scholar]
  11. Puchlik, M.; Ignatowicz, K. Seasonal Changes in Quality of Wastewater from Fruit and Vegetable Industry. E3S Web Conf. 2017, 22, 00139. [Google Scholar] [CrossRef] [Green Version]
  12. Uddin, M.E.; Larson, R.A.; Wattiaux, M.A.E. Ects of dairy cow breed and dietary forage on greenhouse gas emissions from manure during storage and after field application. J. Clean. Prod. 2020, 270, 122461. [Google Scholar] [CrossRef]
  13. Wattiaux, M.A.; Uddin, M.E.; Letelier, P.; Jackson, R.D.; Larson, R.A. Invited Review: Emission and mitigation of greenhouse gases from dairy farms: The cow, the manure, and the field. Appl. Anim. Sci. 2019, 35, 238–254. [Google Scholar] [CrossRef]
  14. Xue, B.; Wang, L.; Yan, T. Methane emission inventories for enteric fermentation and manure management of yak, buffalo and dairy and beef cattle in China from 1988 to 2009. Agric. Ecosyst. Environ. 2014, 195, 202–210. [Google Scholar] [CrossRef]
  15. Kozłowski, K.; Dach, J.; Lewicki, A.; Malińska, K.; Do Carmo, I.E.P.; Czekała, W. Potential of biogas production from animal manure in Poland. Arch. Environ. Prot. 2019, 45, 99–108. [Google Scholar]
  16. Czubaszek, R. Exchange of Carbon Dioxide between the Atmosphere and the Maize Field Fertilized with Digestate from Agricultural Biogas Plant. J. Ecol. Eng. 2019, 20, 145–151. [Google Scholar] [CrossRef]
  17. Haczykowski, M. Evaluation of Selected Biogas Plants in Terms of Feedstock Management. Master’s Thesis, Bialystok University of Technology, Białystok, Poland, 2019; pp. 76–78. [Google Scholar]
  18. Renewable Energy—Recast to 2030 (RED II) EU Science Hub. Available online: https://ec.europa.eu/jrc/en/jec/renewable-energy-recast-2030-red-ii (accessed on 10 October 2020).
  19. Piñas, J.A.V.; Venturini, O.J.; Silva Lora, E.E.; del Olmo, O.A.; Calle Roalcaba, O.D. An economic holistic feasibility assessment of centralized and decentralized biogas plants with mono-digestion and co-digestion systems. Renew. Energy 2019, 139, 40–51. [Google Scholar] [CrossRef]
  20. Sadecka, Z.; Suchowska-Kisielewicz, M. Co-fermentation of chicken manure. Annu. Set Environ. Prot. 2016, 18, 609–625. [Google Scholar]
  21. Vega, G.C.C.; Hoeve, M.; Birkved, M.; Sommer, S.G.; Bruun, S. Choosing co-substrates to supplement biogas production from animal slurry—A life cycle assessment of the environmental consequences. Bioresour. Technol. 2014, 171, 410–420. [Google Scholar] [CrossRef] [PubMed]
  22. Wang, Y.; Zhang, W.; Dong, H.; Zhu, Z.; Li, B. Performance Evaluation of a Large-Scale Swine Manure Mesophilic Biogas Plant in China. Trans. ASABE 2017, 60, 1713–1720. [Google Scholar] [CrossRef]
  23. Konieczny, R.; Łaska, B. The production capacity of renewable energy from available biomass including available tech-nologies. J. Res. Appl. Agric. Eng. 2014, 59, 120–123. [Google Scholar]
  24. Deublein, D.; Steinhauser, A. Biogas from Waste and Renewable Resources; John Wiley & Sons: Hoboken, NJ, USA, 2008; pp. 20–399. [Google Scholar]
  25. Bień, J.D.; Bień, B. Agricultural Biogas Plant as an Element of Waste Management Plant and Green Energy Production in Local Municipality. Eng. Prot. Environ. 2021, 13, 17–27. [Google Scholar]
  26. Maragkaki, A.; Fountoulakis, M.; Kyriakou, A.; Lasaridi, K.; Manios, T. Boosting biogas production from sewage sludge by adding small amount of agro-industrial by-products and food waste residues. Waste Manag. 2018, 71, 605–611. [Google Scholar] [CrossRef] [PubMed]
  27. Czekała, W.; Dach, J.; Dong, R.; Janczak, D.; Malińska, K.; Jóźwiakowski, K.; Smurzyńska, A.; Cieślik, M. Composting potential of the solid fraction of digested pulp produced by a biogas plant. Biosyst. Eng. 2017, 160, 25–29. [Google Scholar] [CrossRef]
  28. Saber, M. Designing biogas units for cleaner energy production from different wastewater effluents. Desalin. Water Treat. 2015, 57, 1–7. [Google Scholar] [CrossRef]
  29. Paramaguru, G.; Kannan, M.; Senthilkumar, N.; Senthilkumar, N.; Lawrence, P. Effect of temperature on biogas produc-tion from food waste through anaerobic digestion. Desalin. Water Treat. 2017, 85, 68–72. [Google Scholar] [CrossRef]
  30. European Biogas Association. Biogas and Biomethane Report; European Biogas Association: Brussels, Belgium, 2015; Available online: http://european-biogas.eu/wp-content/uploads/2016/02/EBA-Annual-Report-2015-Web.pdf (accessed on 28 November 2018).
  31. Lozanovski, A.; Lindner, J.P.; Bos, U. Environmental evaluation and comparison of selected industrial scale biomethane production facilities across Europe. Int. J. Life Cycle Assess. 2014, 19, 1823–1832. [Google Scholar] [CrossRef]
  32. Börjesson, P.; Tufvesson, L.M. Agricultural crop-based biofuels—Resource efficiency and environmental performance in-cluding direct land use changes. J. Clean. Prod. 2011, 19, 108–120. [Google Scholar] [CrossRef]
  33. Appels, L.; Lauwers, J.; Degrève, J.; Helsen, L.; Lievens, B.; Willems, K.A.; Van Impe, J.; Dewil, R. Anaerobic digestion in global bio-energy production: Potential and research challenges. Renew. Sustain. Energy Rev. 2011, 15, 4295–4301. [Google Scholar] [CrossRef]
  34. Weiland, P. Biogas production: Current state and perspectives. Appl. Microbiol. Biotechnol. 2010, 85, 849–860. [Google Scholar] [CrossRef]
  35. Ioelovich, M. Recent findings and the energetic potential of plant biomass as a renewable source of biofuels—A review. Bioresources 2015, 10, 1879–1914. [Google Scholar]
  36. Ahlberg-Eliasson, K.; Nadeau, E.; Levén, L.; Schnürer, A. Production efficiency of Swedish farm-scale biogas plants. Biomass Bioenergy 2017, 97, 27–37. [Google Scholar] [CrossRef]
  37. White, E.M.; Latta, G.; Alig, R.J.; Skog, K.E.; Adams, D.M. Biomass production from the US forest and agriculture sectors in support of a renewable electricity standard. Energy Policy 2013, 58, 64–74. [Google Scholar] [CrossRef]
  38. Maj, G.; Piekarski, W.; Kowalczyk-Juśko, A.; Łukaszczyk, A. Waste from agri-food sector, communal and targeted crops as a source of biogas. Przemysł Chem. 2014, 93, 732–736. [Google Scholar]
  39. Almomani, F.; Bhosale, R.R. Enhancing the production of biogas through anaerobic co-digestion of agricultural waste and chemical pre-treatments. Chemosphere 2020, 25, 126805. [Google Scholar] [CrossRef]
  40. Ibrahim, U.M.; Ahmed, S.I.; Gutti, B.; Muhammad, I.M.; Hamza, U.D.; Ibrahim, M.D. Biogas Production from Combined Irish Potato and Poultry Wastes: Optimization and Kinetic Studies. Int. J. Eng. Technol. 2018, 7, 170. [Google Scholar] [CrossRef] [Green Version]
  41. Han, Y.; Green, H.; Tao, W. Reversibility of propionic acid inhibition to anaerobic digestion: Inhibition kinetics and micro-bial mechanism. Chemosphere 2020, 255, 126840. [Google Scholar] [CrossRef]
  42. Dach, Z.; Zbytek, Z.; Pilarski, K.; Adamski, M. Perspectives and problems of agricultural biogas plants development in Poland. Tech. Rol. Ogrod. Leśna 2009, 6, 2–4. [Google Scholar]
  43. Kozłowski, K.; Lewicki, A.; Cieslik, M.; Janczak, D.; Czekała, W.; Smurzyńska, A.; Brzoski, M. The possibility of improv-ing the energy and economic balance of agricultural biogas plant. Tech. Rol. Ogrod. Leśna 2017, 3, 10–13. [Google Scholar]
  44. Ryckebosch, E.; Drouillon, M.; Vervaeren, H. Techniques for trans-formation of biogas to biomethane. Biomass Bioenergy 2011, 35, 1633–1645. [Google Scholar] [CrossRef]
  45. Batlle-Vilanova, P.; Rovira-Alsina, L.; Puig, S.; Balaguer, M.D.; Icaran, P.; Monsalvo, V.M.; Rogalla, F.; Colprim, J. Biogas upgrading, CO2 valorisation and economic revaluation of bio-electrochemical systems through anodic chlorine production in the framework of wastewater treatment plants. Sci. Total Environ. 2019, 690, 352–360. [Google Scholar] [CrossRef] [PubMed]
  46. Bocci, E.; Di Carlo, A.; McPhail, S.J. Biomass to fuel cells state of the art: A review of the most innovative technology solu-tions. Int. J. Hydrogen Energy 2014, 39, 21876–21895. [Google Scholar] [CrossRef]
  47. Hamawand, I. Anaerobic digestion process and bio-energy in meat industry: A review and a potential. Renew. Sustain. Energy Rev. 2015, 44, 37–51. [Google Scholar] [CrossRef]
  48. Masłoń, A.; Czarnota, J.; Szaja, A.; Szulżyk-Cieplak, J.; Łagód, G. The Enhancement of Energy Efficiency in a Wastewater Treatment Plant through Sustainable Biogas Use: Case Study from Poland. Energies 2020, 13, 6056. [Google Scholar] [CrossRef]
  49. Masłoń, A. An Analysis of Sewage Sludge and Biogas Production at the Zamość WWTP. In Proceedings of the 17th International Scientific Conference on Current Issues of Civil and Environmental Engineering Lviv-Kosice-Rzeszow (CEE), Lviv, Ukraine, 11–13 September 2019. [Google Scholar]
  50. Szczyrba, P.; Masłoń, A.; Czarnota, J.; Olszewski, K. Analysis of sewage sludge and biogas-energy management at the Opole wastewater treatment plant. Inżynieria Ekol. 2020, 21, 26–34. [Google Scholar] [CrossRef]
  51. Kowalczyk-Juśko, A.; Listosz, A.; Flisiak, M. Spatial and social conditions for the location of agricultural biogas plants in Poland (case study). In Proceedings of the 1st International Scientific Conference on Ecological and Environmental Engineering, Krakow, Poland, 26–29 June 2018; Volume 86. [Google Scholar]
Energies 14 03157 g001 550
Figure 1. Biogas plants in Poland: (a) agricultural biogas plant No. 3, (b) scheme agricultural biogas plant No. 3, and (c) biogas plant No. 2 in a sewage treatment plant, (d) scheme biogas plant No. 2 in a sewage treatment plant.
Figure 1. Biogas plants in Poland: (a) agricultural biogas plant No. 3, (b) scheme agricultural biogas plant No. 3, and (c) biogas plant No. 2 in a sewage treatment plant, (d) scheme biogas plant No. 2 in a sewage treatment plant.
Energies 14 03157 g001
Energies 14 03157 g002 550
Figure 2. Mass and volume of charges used in biogas plants. Source: own study based on data from biogas plants, t—agricultural biogas plants, m3—biogas plant No. 2.
Figure 2. Mass and volume of charges used in biogas plants. Source: own study based on data from biogas plants, t—agricultural biogas plants, m3—biogas plant No. 2.
Energies 14 03157 g002
Energies 14 03157 g003 550
Figure 3. Amount of biogas produced in three biogas plants compared with the amount of substrates used.
Figure 3. Amount of biogas produced in three biogas plants compared with the amount of substrates used.
Energies 14 03157 g003
Energies 14 03157 g004 550
Figure 4. Obtained amounts of biogas per 1 ton or 1 m3 of substrates, where dashed red line indicates the yield of m3 biogas from 1 m3 dry sludge.
Figure 4. Obtained amounts of biogas per 1 ton or 1 m3 of substrates, where dashed red line indicates the yield of m3 biogas from 1 m3 dry sludge.
Energies 14 03157 g004
Energies 14 03157 g005 550
Figure 5. Volume of electricity and heat production in biogas plants No. 1, No. 2, and No. 3 in 2018.
Figure 5. Volume of electricity and heat production in biogas plants No. 1, No. 2, and No. 3 in 2018.
Energies 14 03157 g005
Energies 14 03157 g006 550
Figure 6. Amount of feedstock used to generate 1 MW of energy.
Figure 6. Amount of feedstock used to generate 1 MW of energy.
Energies 14 03157 g006
Table
Table 1. Amount of solid substrates fed biogas plant No. 1 in 2018.
Table 1. Amount of solid substrates fed biogas plant No. 1 in 2018.
Month 2018Total Silage (t)Manure (t)Apple Pomace (t)Potato Pulp (t)Others (t)UPPZ Cat. 2 Stomach Contents (t)Total Solid Substrates (mln t)Total Liquid Substrates [t]
I113565.00353.5024.112631073
II106783.001517.626.31209864.0
III944.064.005.0022.21035884.0
IV725.080.0030028.6863.6799.0
V1194133040026.61393751.0
VI127470.000030.41374718.0
VII124070.000020.31330849.0
VIII996.041.015.004.5023.31080847.0
IX101812.017001.0023.21224788.0
X820.016.05750024.41435945.0
XI767.067.06260029.21489905.0
XII892.064.050051013.01520782.0
Sum12,072765188617627.029215,21710,204
Table
Table 2. Characteristics of selected biogas plants. Source: Own study based on data from biogas plants.
Table 2. Characteristics of selected biogas plants. Source: Own study based on data from biogas plants.
Biogas PlantsType of Feedstock UsedAmount of Input Material
[t/Day]		Fermentation Chamber Volume
[m3]		Volume of Biogas Tanks
[m3]		Biogas Management
1Corn silage, manure, liquid manure, fruit pomace, mulch, stomach contents, potato pulp622 × 4.241
6.433		Depends on the fermenter filling levelCo-generators:
400 kW, 600 kW
2Crude sludge, excessive active sludge, co-ferment474 × 7.7005.000Co-generation: 2xJENBACHER JMS 312 GS-B/N.L.; 530 kW each;
HORUS HE-sec 480/510; 480-B, 480 kW each;
Combustion: 2xVITOPLEX 300, 1.400 kW each
3Liquid manure, chicken manure, slaughterhouse and dairy fleet, poultry feathers, cheese whey, vegetable matter, stomach contents982 × 3.200
770		500Co-generator: 0.99 MW el
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Share and Cite

MDPI and ACS Style

Piekutin, J.; Puchlik, M.; Haczykowski, M.; Dyczewska, K. The Efficiency of the Biogas Plant Operation Depending on the Substrate Used. Energies 2021, 14, 3157. https://doi.org/10.3390/en14113157

AMA Style

Piekutin J, Puchlik M, Haczykowski M, Dyczewska K. The Efficiency of the Biogas Plant Operation Depending on the Substrate Used. Energies. 2021; 14(11):3157. https://doi.org/10.3390/en14113157

Chicago/Turabian Style

Piekutin, Janina, Monika Puchlik, Michał Haczykowski, and Katarzyna Dyczewska. 2021. "The Efficiency of the Biogas Plant Operation Depending on the Substrate Used" Energies 14, no. 11: 3157. https://doi.org/10.3390/en14113157

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop