Abstract
Herein a techno-economic assessment was performed on an energy-crop-based biogas plant coupled with a greenhouse for utilizing thermal energy produced by cogeneration. Seven energy crops were evaluated: triticale, maize, alfalfa, sunflower, clover, barley and wheat. According to the evaluation, triticale was the most competitive energy crop under selected climate conditions for northern Greece. Although maize displays higher biomass yield and biogas potential than the drought-resistant crop triticale, it has high irrigation demand that contributes significantly to total production costs. For a triticale-based biogas production to become economically feasible, agricultural arable area larger than 500 ha, or biogas plant size larger than 1000 kWel, is required. However, with public funding, biogas production becomes feasible at smaller area (>250 ha) or biogas plant size (>500 kWel). The inclusion of a greenhouse into the design of the biogas plant contributes positively to the economic viability of the entire system. Under this scenario, greenhouse financial income accounts for about 17–18% of total income. Results of a sensitivity analysis suggest that the selection of an appropriate energy crop for biogas production should be based principally on both digestibility (specific methane yield) and biomass yield per hectare, these factors being more critical than biomass production costs.
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Abbreviations
- C :
-
Constant accounting for material properties of the pump
- \(C_{{{\text{CH}}_{4} }}\) :
-
Specific methane yield (m3 CH4/t VS)
- C DM :
-
Dry matter content of silage (%FM/100)
- C G :
-
Specific investment costs (€/m2)
- C R :
-
Carriage capacity of the tractor (m3)
- C VS :
-
Volatile solids content of dry mass (%DM/100)
- D :
-
Inner diameter of the tube (mm)
- D d :
-
Day duration (h)
- d IT :
-
Depth of tillage (cm)
- D n :
-
Night duration (h)
- D S :
-
Depth of implement in the soil (cm)
- d T :
-
Total distance travelled by the tractors (km)
- H E :
-
Operational manometric pressure of equipment (m)
- H L :
-
Pressure losses in the pipes (m)
- H T :
-
Total manometric water pressure (m)
- H W :
-
Depth of the water body from which water is pumped (m)
- k AV :
-
Availability rate of biomass within the operational radius, here: 0.3
- k FA :
-
Unplanted, fallow land coefficient
- k LO :
-
Factor accounting for losses in harvesting and silaging
- k P :
-
Specific power requirements of each implement (kW/(mIW × (km/h))
- k PL :
-
Partial load operation factor (%)
- k PM :
-
Coefficient for safety margin in tractor engine sizing
- k T :
-
Factor to include tractor turns on the fields
- k UN :
-
Un-arable land area coefficient
- M BD :
-
Dry mass of crops to be packed (t DM)
- M BF :
-
Fresh mass of crop biomass transported (t)
- M TT :
-
Transportation capacity of the tractors (t)
- N :
-
Month of the year in the cultivation period (September–July)
- N H :
-
Hourly diesel fuel consumptions for each field work (L/h)
- NPV:
-
Net present value (€)
- n R :
-
Number of reactors in the biogas plant
- n TT :
-
Number of tractors required for biomass transportation
- n TF :
-
Number of tractors required for field works
- N T :
-
Total fuel consumption of tractors (L)
- P :
-
Value of yearly cash flow at the year showing first positive value of cumulative cash flow
- PBP:
-
Payback period (year)
- P D :
-
Drawbar power (kW)
- P E :
-
Engine power per tractor (kW)
- P EC :
-
Cumulated engine power of all tractors (kW)
- P EE :
-
Electrical power of the engine (kW)
- P P :
-
Pump power required to drive water sprinklers (kW)
- P TO :
-
Power-take-off (kW)
- P TT :
-
Engine power of transport tractors (kW)
- Q :
-
Water flow for irrigation (m3/h)
- R A :
-
Ratio of direct availability of nutrients in digestates (%)
- R E :
-
Ratio of fertilizing efficiency (%)
- r e :
-
Pump efficiency coefficient
- R FERT :
-
Recycling rate of nutrients related to the spreading of digestate onto the fields (%)
- R L :
-
Nutrient losses during storage of the digestates
- R S :
-
Soil resistance (N/(m × cmDS))
- r SIL :
-
Packing rate (h/t DM)
- r U :
-
Engine power usage factor
- S C :
-
Operational cultivation area, after subtraction of un-arable land and fallow land (ha)
- S G :
-
Greenhouse surface (ha)
- S L :
-
Total cultivation area, including un-arable land and fallow land (ha)
- T A :
-
Duration available to perform ploughing operations (h)
- T d :
-
Target day temperature in the month (°C)
- T D :
-
Total distance covered by tractors for biomass transportation (km)
- T HD :
-
Day heating degrees (°C)
- T HN :
-
Night heating degrees (°C)
- T iav :
-
Average day temperature in the month (°C)
- T imax :
-
Maximum day temperature in the month (°C)
- T n :
-
Target night temperature in the month (°C)
- t SIL :
-
Operation time of packing tractors for silaging (h)
- t W :
-
Time required to perform each individual field operation (h)
- V :
-
Total volume of biomass to be transported (m3)
- v :
-
Value of cumulative cash flow at year showing last negative value of cumulative cash flow (€)
- v T :
-
Tractor velocity (km/h)
- v TT :
-
Average speed of the transport tractors (km/h)
- W I :
-
Size of implements used for tillage and other field operations (m)
- W IT :
-
Size of the ploughing implement attached to the tractor (m)
- Y BF :
-
Fresh biomass yield before ensiling (t/ha)
- \(Y_{{{\text{CH}}_{4} }}\) :
-
Methane yields per hectare (m3 CH4/ha)
- Y E :
-
Electrical efficiency of CHP unit (%)
- Y N :
-
Years after initial investment showing the last negative value of cumulative cash flow (year)
- Y SD :
-
Yield of dry ensiled biomass (t DM/ha)
- Y TH :
-
Thermal efficiency (%)
- ΔT SUN :
-
Indoor/outdoor temperature difference due to greenhouse effect (°C)
- τ :
-
Tortuosity factor
References
Konrad C et al (2011) Bioenergy for regions—alternative cropping systems and optimisation of local heat supply, energy and sustainability. III. In: Villacampa Y, Brebbia CA, Mammoli AA (eds) 3rd international conference on energy and sustainability, Alicante, Spain, 11–13, Apr 2011. WIT Press, Southampton
Amigun B, von Blottnitz H (2010) Capacity-cost and location-cost analyses for biogas plants in Africa resources. Conserv Recycl 55:63–73. doi:10.1016/j.resconrec.2010.07.004
Balussou D, Kleyböcker A, McKenna R, Möst D, Fichtner W (2012) An economic analysis of three operational co-digestion biogas plants in Germany. Waste Biomass Valoriz 3:23–41
Balussou D, Heffels T, McKenna R, Möst D, Fichtner W (2014) An evaluation of optimal biogas plant configurations in Germany. Waste Biomass Valoriz 5:743–758
Barbanti L, Di Girolamo G, Grigatti M, Bertin L, Ciavatta C (2014) Anaerobic digestion of annual and multi-annual biomass crops. Ind Crops Prod 56:137–144. doi:10.1016/j.indcrop.2014.03.002
Braun R, Weiland P, Wellinger A (2008) Biogas from energy crop digestion. In: IEA bioenergy task, pp 1–20
Brulé M (2014) The effect of enzyme additives on the anaerobic digestion of energy crops. Ph.D. thesis. VDI-MEG 538. State Institute of Agricultural Engineering and Bioenergy, University of Hohenheim. http://opus.uni-hohenheim.de/volltexte/2014/1030/
Brulé M, Bolduan R, Seidelt S, Schlagermann P, Bott A (2013) Modified batch anaerobic digestion assay for testing efficiencies of trace metal additives to enhance methane production of energy crops. Environ Technol 34:1–12
Buckmaster D (2009) Equipment matching for silage harvest. Appl Eng Agric 25:31–36
D’Amours L, Savoie P (2005) Density profile of corn silage in bunker silos. Can Biosyst Eng 47:21–28
Davies B (2004) Assessing the economics of silage production. In: Kaiser AG, Piltz JW, Burns HM, Griffiths NW (eds) Successful silage. NSW Department of Primary Industries, Orange,, pp. 277–310. http://www.dpi.nsw.gov.au. Retrieved 20 Oct 2015
de Castro Villela IA, Silveira JL (2005) Thermoeconomic analysis applied in cold water production system using biogas combustion. Appl Therm Eng 25:1141–1152. doi:10.1016/j.applthermaleng.2004.08.014
Dion L-M, Lefsrud M, Orsat V (2011) Review of CO2 recovery methods from the exhaust gas of biomass heating systems for safe enrichment in greenhouses. Biomass Bioenergy 35:3422–3432. doi:10.1016/j.biombioe.2011.06.013
Esen M, Yuksel T (2013) Experimental evaluation of using various renewable energy sources for heating a greenhouse. Energy Build 65:340–351. doi:10.1016/j.enbuild.2013.06.018
EurObserve’ER (2014) Biogas barometer. Biogas electricity production growth in 2013. www.eurobserv-er.org/. Retrieved 10 Apr 2015
Faaij APC (2006) Bio-energy in Europe: changing technology choices. Energy Policy 34:322–342. doi:10.1016/j.enpol.2004.03.026
Fierro J, Gómez X, Murphy JD (2014) What is the resource of second generation gaseous transport biofuels based on pig slurries in Spain? Appl Energy 114:783–789. doi:10.1016/j.apenergy.2013.08.024
FNR (2013) Leitfaden Biogas—Von der Gewinnung zur Nutzung (Biogas handbook - From production to valorization). Fachagentur Nachwachsende Rohstoffe e.V. (FNR), Gülzow, Germany
Gabrielle B et al (2014) Paving the way for sustainable bioenergy in Europe: technological options and research avenues for large-scale biomass feedstock supply. Renew Sustain Energy Rev 33:11–25. doi:10.1016/j.rser.2014.01.050
Gissén C et al (2014) Comparing energy crops for biogas production—yields, energy input and costs in cultivation using digestate and mineral fertilisation. Biomass Bioenergy 64:199–210. doi:10.1016/j.biombioe.2014.03.061
Grieb B, Gerlach F (2013) BioBiogas—Erfahrungen bei der Erzeugung von Biogas im Ökologischem Landbau [Experiences from biogas production in organic farming] Der kritische Agrarbericht, pp 102–108
Harrigan T (2003) Time-motion analysis of corn silage harvest systems. Appl Eng Agric 19:389–396
Herrmann A (2013) Biogas production from maize: current state, challenges and prospects. 2. Agron Environ Asp Bioenergy Res 6:372–387
Herrmann C, Prochnow A, Heiermann M, Idler C (2012) Particle size reduction during harvesting of crop feedstock for biogas production. II: effects on energy balance, greenhouse gas emissions and profitability. BioEnergy Res 5:937–948. doi:10.1007/s12155-012-9207-1
Hublin A, Schneider DR, Džodan J (2014) Utilization of biogas produced by anaerobic digestion of agro-industrial waste: energy, economic and environmental effects. Waste Manag Res. doi:10.1177/0734242x14539789
Jaffrin A, Bentounes N, Joan AM, Makhlouf S (2003) Landfill biogas for heating greenhouses and providing carbon dioxide supplement for plant growth. Biosyst Eng 86:113–123. doi:10.1016/S1537-5110(03)00110-7
Jílek L, Pražan R, Podpěra V, Gerndtová I (2008) The effect of the tractor engine rated power on diesel fuel consumption during material transport. Res Agric Eng 54:1–8
Jones P, Salter A (2013) Modelling the economics of farm-based anaerobic digestion in a UK whole-farm context. Energy Policy 62:215–225. doi:10.1016/j.enpol.2013.06.109
Katerji N, Mastrorilli M, Rana G (2008) Water use efficiency of crops cultivated in the Mediterranean region: review and analysis. Eur J Agron 28:493–507. doi:10.1016/j.eja.2007.12.003
KTBL (2009) Faustzahlen Biogas—2. Auflage (Key figures for biogas—2nd edition). Kuratorium für Technik und Bauwesen in der Landwirtschaft, Damstadt
Kusch S (2012) Biogas grids—An intelligent element in efficient utilisation of renewable energy. International virtual conference, section 12 industrial and civil engineering, 03–07 Dec 2012, pp 1823–1826
Mast B, Lemmer A, Oechsner H, Reinhardt-Hanisch A, Claupein W, Graeff-Hönninger S (2014) Methane yield potential of novel perennial biogas crops influenced by harvest date. Ind Crops Prod 58:194–203
Mavrogiannopoulos G (2005) Greenhouses - Environment, materials, construction, equipment. Stamoulis, Athens (in Greek). ISBN-13 978-960-351-620-0
Mehta CR, Singh K, Selvan MM (2011) A decision support system for selection of tractor—implement system used on Indian farms. J Terrramech 48:65–73. doi:10.1016/j.jterra.2010.05.002
Menardo S et al (2013) Biogas production from steam-exploded miscanthus and utilization of biogas energy and CO2 in greenhouses. Bioenergy Res 6:620–630
Möller K, Schulz R, Müller T (2012) Substrate inputs, nutrient flows and nitrogen loss of two centralized biogas plants in southern Germany. Nutr Cycl Agroecosyst 87:307–325
NSW-Farmers (2013) Estimating tractor power needs. NSW (New South Wales) Farmers Association. www.nswfarmers.org.au. Retrieved 19 Oct 2014
Panepinto D, Viggiano F, Genon G (2014) The potential of biomass supply for energetic utilization in a small Italian region: Basilicata. Clean Technol Environ Policy 16:833–845. doi:10.1007/s10098-013-0675-6
Pöschl M, Ward S, Owende P (2010) Evaluation of energy efficiency of various biogas production and utilization pathways. Appl Energy 87:3305–3321
Raposo F, De la Rubia MA, Fernández-Cegrí V, Borja R (2012) Anaerobic digestion of solid organic substrates in batch mode: an overview relating to methane yields and experimental procedures. Renew Sustain Energy Rev 16:861–877
Šarauskis E, Buragienė S, Masilionytė L, Romaneckas K, Avižienytė D, Sakalauskas A (2014) Energy balance, costs and CO2 analysis of tillage technologies in maize cultivation. Energy 69:227–235. doi:10.1016/j.energy.2014.02.090
Schievano A, D’Imporzano G, Orzi V, Colombo G, Maggiore T, Adani F (2015) Biogas from dedicated energy crops in Northern Italy: electric energy generation costs GCB Bioenergy 7:899–908. doi:10.1111/gcbb.12186
Seppälä M, Paavola T, Lehtomäki A, Rintala J (2009) Biogas production from boreal herbaceous grasses—specific methane yield and methane yield per hectare. Bioresour Technol 100:2952–2958
Sitkey V, Gaduš J, Kliský Ľ, Dudák A (2013) Biogas production from Amaranth biomass. Acta Reg Environ 10:59–62
Stürmer B, Schmid E, Eder MW (2011) Impacts of biogas plant performance factors on total substrate costs. Biomass Bioenergy 35:1552–1560. doi:10.1016/j.biombioe.2010.12.030
Summer P, Williams E (2014) What size farm tractor do I need? University of Georgia, College of Agriculture, GA, USA and U. S. Department of Agriculture. www.caes.uga.edu. Retrieved 20 Oct 2015
Taricska J, Long D, Chen JP, Hung Y-T, Zou S-W (2009) Anaerobic Digestion. In: Wang L, Pereira N, Hung Y-T (eds) Biological treatment processes, vol 8. Handbook of environmental engineering. Humana Press, pp 589–634. doi:10.1007/978-1-60327-156-1_14
Terzidis GA, Papazafeiriou ZG (1997) Agricultural hydraulics. Ziti S.A., Thessaloniki (in Greek)
Torquati B, Venanzi S, Ciani A, Diotallevi F, Tamburi V (2014) Environmental sustainability and economic benefits of dairy farm biogas energy production: a case study in Umbria. Sustainability 6:6696
Tuck G, Glendining MJ, Smith P, House JI, Wattenbach M (2006) The potential distribution of bioenergy crops in Europe under present and future climate. Biomass Bioenergy 30:183–197. doi:10.1016/j.biombioe.2005.11.019
Vallios I, Tsoutsos T, Papadakis G (2009) Design of biomass district heating systems. Biomass Bioenergy 33:659–678. doi:10.1016/j.biombioe.2008.10.009
Venturi P, Venturi G (2003) Analysis of energy comparison for crops in European agricultural systems. Biomass Bioenergy 25:235–255
von Elsner B et al (2000) Review of structural and functional characteristics of greenhouses in European Union countries. Part II: typical designs. J Agric Eng Res 75:111–126. doi:10.1006/jaer.1999.0512
Walla C, Schneeberger W (2008) The optimal size for biogas plants. Biomass Bioenergy 32:551–557. doi:10.1016/j.biombioe.2007.11.009
Weiland P (2010) Biogas production: current state and perspectives. Appl Microbiol Biotechnol 85:849–860
Wilson DM et al (2014) Establishment and short-term productivity of annual and perennial bioenergy crops across a landscape gradient. BioEnergy Research 7:885–898
Wünsch K, Gruber S, Claupein W (2012) Profitability analysis of cropping systems for biogas production on marginal sites in southwestern Germany. Renew Energy 45:213–220. doi:10.1016/j.renene.2012.03.010
Zegada-Lizarazu W, Monti A (2011) Energy crops in rotation. A review. Biomass Bioenergy 35:12–25
Acknowledgements
This work was partially funded by the Greek Public Properties Company S.A., in the framework of a research contract between the company and the Agricultural University of Athens. Mathieu Brulé has been granted a Ph.D. scholarship from the Faculty of Agricultural Sciences of the University of Hohenheim that helped him contribute to this work; Mathieu Brulé would like to thank Dr. Hans Oechsner and Prof. Thomas Jungbluth for supervising his Ph.D. thesis.
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Appendices
Appendix 1
Equation for section “Total land area”
Total land area (S L) is given from the operational cultivation area (S C) by the following equation:
Equations for section “Engine power, number of tractors and fuel consumption for cultivation”
The required size of the ploughing implement (W IT) attached to the tractor was calculated according to the following equation:
S C operational cultivation area (ha), T A duration available to perform ploughing operations, here: 160 h, v T tractor velocity (km/h), here 6 km/h for ploughing operation.
Drawbar power (P D; kW) corresponding to the selected implement size is calculated and converted into power-take-off (P TO; kW), and engine power for tillage (P EP; kW) applying the following equation and conversion factors (Mehta et al. 2011; NSW-Farmers 2013):
R S soil resistance, here: 890 N/(mIW × cmDS), d IT depth of tillage (plough), here: 20 cm, W IT width of implement used for tillage (plough), v T tractor velocity, here: 6 km/h, k PM additional factor providing a safety margin in tractor sizing, here: 10%
Linear correlation between total engine power (P EP; kW) and the surface of cultivated area (S C; ha) is described by the following eq.:
Specific power requirements [k P; (kW/(mIW × (km/h))] of each implement were calculated with the following equation, with values for the factors R s and D I taken from Table 8.
Time (t W; h) required to perform each individual field operation is given by the following equations, according to the total distance travelled by the tractors (d T; km):
k T factor to include tractor turns on the fields, here: 1%, W I width (m) of each implement, r U engine power usage, set at 0.8 (80%) to prevent engine overloading (Mehta et al. 2011).
Hourly diesel fuel consumptions (N H; L/h) for each field work were estimated using the empirical equation given by Jílek et al. (2008). Subsequently, the total fuel consumption (N T; L) of tractors was calculated for the work durations (t W; h) estimated previously for each field work:
where P E is for the engine power (kW).
Equations for section “Irrigation and fertilizing of energy crops”
Pump power (P P; kW) required to drive the sprinklers was calculated from the total manometric water pressure (H T, m), accounting for pressure losses in the pipes (H L, m) (Terzidis and Papazafeiriou 1997):
H E operational manometric pressure of equipment, here: 80 m, H W depth of the water body from which water is pumped, here: 10 m, Q water flow (m3/h), depends on irrigation requirements, r e pump efficiency, set at 70% (Buckmaster 2009), C constant depending on material properties, here: 150 (Terzidis and Papazafeiriou 1997), D inner diameter of the tube (mm).
Total fertilization requirements:
R E fertilizing efficiency (here: 80%), R L nutrient losses during storage of the digestates, here: 35%, R A direct availability of nutrients in digestates, here: 70%.
Equations for section “Transportation and silaging of energy crops and digestates”
Transport distance of harvested biomass to bunker silos was calculated by:
d T haul distance (km), τ tortuosity factor, here: 1.8, M BF fresh mass of crop biomass (t) to be transported, k AV availability of biomass, here: 0.3, Y BF fresh biomass yield before ensiling (t/ha).
The total distance (T D; km) that the tractor(s) need to cover transportations was calculated as follows:
V total volume of biomass to be transported (m3), C R Carriage capacity of the tractor (m3): here 18 m3.
The number of tractors required for biomass transportation (nT) was calculated according to:
n T number of tractors required, P TT engine power of transport tractors (kW), M TT transportation capacity of the tractors, here: 20 t of dry matter, v TT average speed of the transport tractors, here: 20 km/h.
The operation time of packing tractors for silaging (t SIL) was calculated as
r SIL packing rate, here: 0.017 h/t DM, M BD dry mass of crops to be packed (t DM).
Equations for section “Methane yields of energy crops”
Yields of dry ensiled biomass (Y SD; t DM/ha) are calculated for each crop:
Y BF yield of fresh biomass (t FM/ha), k LO factor accounting for losses in harvesting and silaging, here: 13% (Davies 2004), C DM dry matter content of silage (%FM/100).
Yields of dry ensiled biomass are converted into methane yields per hectare (\(Y_{{{\text{CH}}_{4} }}\); m3 CH4/ha):
C VS volatile solids content of dry mass (%DM/100), \(C_{{{\text{CH}}_{4} }}\) specific methane yield (m3 CH4/t VS).
Equations for section “Design of the greenhouse system”
Day heating degrees (T HD; °C) and night heating degrees (T HN; °C) are calculated as follows:
T imax maximum day temperature in the month (°C), T iav average day temperature in the month (°C), T d target day temperature in the month, here: 22 °C, ΔT SUN indoor/outdoor temperature difference due to greenhouse effect, here: 6 °C, T n target night temperature in the month, here: 14 °C, D d day duration (h), D n night duration (h), N month of the year in the cultivation period (September–July).
Specific investment costs (€/m2) of the greenhouse in relation to the surface area were calculated with the following equation (input parameters for economic evaluation cf. “Appendix 2” section):
S G greenhouse surface (ha).
Electrical (Y E; %) and thermal efficiency (Y TH; %) of the CHP unit was calculated with:
P EE electrical power of the engine, k PL partial load operation factor, here: 97%.
Equations for section “Methodology for economic evaluation”
For this purpose, annual cash flow calculations were made using the following equation:
C t net cash inflow during the period t, C 0 total initial investment costs, r discount rate; here 6%, T number of time periods (years).
The PBP was calculated as follows:
Y N number of years after the initial investment at which the last negative value of cumulative cash flow occurs, v value of cumulative cash flow at the year with the last negative value of cumulative cash flow, p value of yearly cash flow at the year with the first positive value of cumulative cash flow.
Appendix 2
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Markou, G., Brulé, M., Balafoutis, A. et al. Biogas production from energy crops in northern Greece: economics of electricity generation associated with heat recovery in a greenhouse. Clean Techn Environ Policy 19, 1147–1167 (2017). https://doi.org/10.1007/s10098-016-1314-9
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DOI: https://doi.org/10.1007/s10098-016-1314-9