Performance and emission characteristics of biogas used in diesel engine operation
Introduction
Mitigating the rapid increase in atmospheric pollution by greenhouse gases is an important problem. Pollution from transport accounts for one fifth of all of the emitted hazardous compounds that contribute to the greenhouse effect. The new European Commission Directive 2009/28/EC was approved, aiming to replace 10% of all fuels consumed in transport with biofuels by 2020. Biogas is a potential renewable energy source if properly prepared and adapted for use in transport vehicles [1]. Raw materials (e.g., agricultural, urban infrastructure and industrial waste; green biomass) exhibit a sufficiently high potential for the production of biogas but are underutilised [2], [3], [4], [5], [6]. The main components of biogas are methane (CH4) and carbon dioxide (CO2). The biogas composition depends on the parameters of the production process and the type and composition of the raw materials [7].
A typical biogas composition is as follows: methane – CH4 (50–75%), carbon dioxide – CO2 (25–45%), nitrogen – N2 (0–10%), hydrogen – H2 (1–2%), hydrogen sulphide – H2S (0–0.5%) and oxygen – O2 (0–2%) [8]. The combustion value of a biogas is directly related to its methane concentration. A biogas containing 60% methane has a calorific value of 21.5 MJ/m3, whereas a biogas with a 96% methane concentration has a calorific value of 35 MJ/m3 [9].
The use of biogas in diesel engines (i.e., for compression ignition) is environmentally beneficial not only because it increases renewable fuel consumption in transport but also because methane is considerably lower in carbon than ordinary diesel fuel; therefore, using biogas can reduce pollutant levels in exhaust gases, including emissions of solid particles and nitrogen oxides [10]. However, biogas cannot be used separately from diesel, a dual-fuel supply system when biogas–biodiesel and biogas–mineral diesel are used as fuel is required [11].
In some countries, biogas is used in urban transport. In Linkoping (Sweden), biogas with methane concentrations of at least 97% is used in 64 buses and heavy and light motor vehicles. In Sweden, the use of biogas since 2002 in urban transport alone has reduced carbon dioxide emissions by 9000 t/y [12].
There is no universal international standard for the quality of the biogas used in the transport sector. Some countries (Germany, France, the Netherlands, Sweden, Austria and Switzerland) have approved national standards for biogas used in transport (see Table 1) [10].
In most countries, the main biogas quality indicator is the methane concentration, which should be at least 96%, and carbon dioxide, which should not exceed 4%. The Wobbe index is another indicator for fuel that depends on higher heating value and can be used as a basis for comparison between different gases. The concentrations of sulphur hydrogen and water vapour in gases are also restricted because reactions of these substances can corrode engines [13]. Gases that comply with the requirements of the standards can be used in diesel engines; however, biogas obtained by anaerobic processing contains excessively high concentrations of sulphur hydrogen and water vapour, and thus does not comply with the requirements of the standards. Sorption technologies can be used to remove biogas from these compounds [14], [15]. Sorption processes require additional consumption of energy and materials. The carbon dioxide concentration in biogas is higher than the corresponding sulphur hydrogen and water vapour concentrations, such that removing carbon dioxide from the biogas accounts for most of the energy and materials consumption. Although the negative impact of sulphur hydrogen and water vapour on corrosiveness are clearly understood, much less is known about the impact of high carbon dioxide concentrations on engine operation and the pollutant concentrations in the exhaust gas. It is absolutely clear that increasing the carbon dioxide concentration decreases the fuel combustion value, thereby increasing fuel consumption; however, the impact of the carbon dioxide concentration on the engine operation remains unclear. If this impact is low, it may be reasonable and economically efficient to only partially remove carbon dioxide or not remove carbon dioxide at all from biogas for use in diesel engines.
The objective of our study was to evaluate the impact of the carbon dioxide concentration in biogas on the operating characteristics and exhaust gas emissions of a diesel engine running on a mixture of biogas and mineral diesel fuel.
Section snippets
Materials and methods
The biogas used in the tests was obtained from a company that trades in various technical and medical grade gases.
Biogases of the following compositions were used in the experiments:
- (1)
95% methane and 5% CO2 (labelled as M95% in the figures);
- (2)
85% methane and 15% CO2 (labelled as M85% in the figures); and
- (3)
65% methane and 35% CO2 (labelled as M65% in the figures).
First composition represents average amount of carbon dioxide in raw biogas produced in anaerobic digesters, second and third composition
Primary tests
The primary tests were performed under the following conditions: the EGR system was switched on or off; the engine speed was 2500 min−1; the torque was varied from 20 to 100 N m in increments of 20 N m; the added biogas contained 95%, 85% and 65% of methane; the gas supply rate was 20 or 40 l/min; and the start of injection timing was set by the engine ECU and was not adjusted.
The tests performed on a conventionally adjusted engine showed that supplying additional biogas amount, the air/fuel ratio is
Conclusions
The tests conducted in this study showed that using biogas in a diesel engine requires certain operational modifications, i.e., the use of an EGR system and the adjustment of the start of injection timing. If the gas was supplied without modifying the engine control system, the total fuel consumption increased, the thermal efficiency decreased, and the concentration of the pollutants, except for NOx, in the exhaust increased.
When the EGR system was turned off, the air/fuel ratio increased, and
Acknowledgments
This work has been supported by the European Social Fund within the project “Development and application of innovative research methods and solutions for traffic structures, vehicles and their flows”, (project code VP1-3.1-SMM-08-K-01-020).
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