BIOFUELS IN THE FUEL INJECTION SYSTEM OF A SINGLECYLINDER MEDIUM-SPEED DIESEL ENGINE AKI TILLI MARTTI LARMI OSSI KAARIO aki.tilli@tkk.fi, tel. 09 451 3463 Internal Combustion Engine Research group TKK Helsinki University of Technology, Helsinki, Finland ABSTRACT As the awareness of the climate change has become widespread and the forthcoming fossil fuel production decline gets closer and closer, the biofuels and their behavior have become one of the most important fields of research in the energy technology sector and as well in the internal combustion engine studies. The diesel-type biofuels are naturally more or less CO2 –neutral. Moreover, in renewable diesel studies also other emissions have been promisingly low. The focus of this research was to evaluate the compatibility of modern renewable diesel fuels with the fuel injection system of the “Extreme Value Engine” (EVE), a singlecylinder medium-speed research engine of the Internal Combustion Engine research group in Otaniemi. In the study, the objective was to determine whether biofuels and especially their physical properties require changes in the fuel injection system. The research consisted of a literature study of biofuels and their comparison, a report on the simulation model designed and the simulations, and of the results and summary presentation. In the literature part, conventional diesel and different renewable diesel-type fuels are introduced. The fuels introduced are traditional biodiesel (fatty acid methyl ester, FAME), hydrotreated vegetable oil (HVO), Fischer-Tropsch (FT) diesel fuels and dimethyl ether (DME). The raw materials, production and characteristics of the fuel types are briefly introduced and their qualities and usability compared. In the simulations part, first the software used (GT-FUEL) is introduced briefly. The simulation model made as a part of the study and the simulations to fit the model to measurements are presented. The simulations to actually compare different fuels in the fuel injection system, the results and the alleged behaviour of the fuels in the EVE fuel injection system are then introduced. According to the simulations, the behavior of different renewable diesel fuels in the fuel system is very similar. Of the physical properties, mainly the differences in fuel densities and viscosities have some predictable effect on the fuel masses injected. The chemical properties of the fuels (which the simulation model does not take into account) are probably more important for the fuel injection system. Fuel spray behavior and combustion of renewable diesels are important research issues and should be the next step in the study of renewable diesel fuels in the EVE research engine. Keywords: Biofuel, Renewable diesel, Biodiesel, Fischer –Tropsch, Dimethyl ether, Hydrotreated vegetable oil FAME, HVO, BTL, GTL, DME, NExBTL, Internal combustion engines, Extreme value engine, Fuel injection, Simulation, GT-FUEL 2 1. INTRODUCTION The goal of this study was to prepare future research of fuel injection and alternative fuels in the Internal Combustion Engine research group by studying different biofuels that have been used in diesel engines, and evaluate their usability in the “Extreme Value Engine” (EVE). The fuels deemed most suitable were traditional biodiesel (fatty acid methyl ester, FAME), hydrotreated vegetable oil (HVO), Fischer-Tropsch (FT) diesel fuels and dimethyl ether (DME). The data required was collected and a simulation model of the fuel injection system of the EVE engine was developed. EVE is a single-cylinder medium-speed 4-stroke diesel engine with a 200 mm bore. The current maximum cylinder pressure of EVE is ~ 200 bar, rail pressure 1400 bar and engine speed 900 rpm. It has a charge air compressor (1-8 bars) and floating engine bed on air springs. Special characteristics include electro-hydraulic control of gas exchange valves, electro-hydraulic control of injection valve, operation in motored mode, easy access for measurements and optical access. The fuel injection system of EVE is based on Wärtsilä W32 common rail accumulator and W20 injector. Especially important in EVE is that it is very flexible and accessible test bed for research purposes with powerful and versatile control of engine parameters. (Lehto K, 2007), (Olenius T, 2006) The simulation model in this study was made with GT-FUEL, an object-oriented fuel injection system simulation program. GT-FUEL is part of the GT-SUITE software family. The simulation model created was first adjusted to measured boundary conditions. Simulations using fuel models based on properties of different biofuels and a standard fossil fuel as a reference were run with different loads. The results were used to evaluate possible changes needed in the fuel injection system. From the fuel injection system simulations, boundary conditions for the CFD calculations concerning fuel spray behaviour and combustion were obtained. Biofuel compatibility with EVE was evaluated and new parameters for the biofuel injection in EVE research engine are being searched for. Eventually, the goal is to find optimum combustion conditions and reach high engine efficiency with significant emission reductions. 2. THE FUELS STUDIED 2.1 Standard diesel fuel Conventional diesel fuel quality requirements are based on international standards. EN 590, partly introduced in table 1., is a standard that determines the physical properties all the diesel fuels sold in EU must fulfill. Table 1. EN 590: standard for diesel fuel in EU. In addition to the EN 590 requirements, the demands of local climate and the Criteria EN 590 users of the fuel set a standard of their Density @ 15°C (g/cm³) 0.82-0.845 Viscosity @ 40°C (mm²/s) 2.0-4.5 own. In this study the focus was on Flashpoint (°C) >55 physical properties, especially on density Cetane number >51 and viscosity. (Mikkonen et al., 2007) 1 2.2 Conventional biodiesel - FAME According to many standards, directives and laws, only the traditional first generation renewable diesels can be called “biodiesel”. These traditional biodiesels consist of fatty acid methyl esters, usually referred to as “FAME”. These fuels comprise of moderately long (C16-C18) fatty acid chains, mainly mono-alkyl fatty acid esters. (Mikkonen et al., 2007), (Mikkonen, 2007) Traditional biodiesel are usually produced by transesterification method from fatty acids by using base as a catalyst. In transesterification processes the triglycerides of the fatty acids react with an alcohol and thus mono alkyl esters and raw glycerol are produced. This reaction only occurs in the presence of a strong base as a catalyst. The most common catalysts used are water-free sodium- or potassium hydroxide. Before they are added to the reactor, the bases are dissolved into the alcohol used in the reaction. The most common alcohol used is _______________________________________ methanol (ca. 10% of the reacting substances). Other alcohols can also be used, if not (yet) as efficiently. (Yamane et al., 2001), (Van Gerpen et al., 2004), (Knothe G, 2005) Thermodynamically, FAME is quite similar to traditional diesel fuels. However, there are differences in chemical behaviour and physical Figure 1. Tr ansesterification reaction. (Van Gerpen et al., properties, especially in density, 2004) viscosity and compressibility. Because of its higher compression modulus, with FAME, the pressure pulsations are faster, the injection starts earlier and the maximum pressure is higher than with traditional diesel at low mean pressures and temperatures (293 – 313 K). With higher injection pressures and temperatures the effect disappears. (Yamane et al., 2001), (Knothe G, 2005), (Mikkonen S, 2007) Traditional biodiesels are non-toxic and biodegradable, their production process is simple and easy, and they are practically free of sulphur and ring-shaped aromatic carcinogens. FAME is mainly produced from renewable or recycled components, usually vegetable oils. Therefore, the impact on greenhouse effect should be smaller when FAME is used rather than pure fossil fuels. Emissions of particles, hydrocarbons, and carbon monoxide also seem to lessen when FAME is used. FAME also improves the lubricity of the fuel mixtures even in small proportions, especially with sulphur -free fuels. However, emissions of NOx, cold smoking, engine oil deterioration, corrosion, and carbon build-up in the fuel injection system seem to increase if 100% FAME is used. Usually the cold operation characteristics of FAME are worse than with a normal diesel fuel and the high boiling range (340-360 °C) has caused problems. Because of these drawbacks, engine manufacturers recommend, that the amo unt of FAME in the fuel should be 5 % (weight) at maximum in the usual diesel engines. Still, even in relatively low quantities, the fatty 2 acids of FAME may harden and embrittle rubber parts (such as seals and hoses) that endure acids badly. FAME-based fuels are difficult to store because of the biodegradability and tendency to gather up water during transportation. Moreover, the best quality-FAME oil (RME, rapeseed methyl ester) is derived from rapeseed oil that is also used in food industry. Thus, its production competes with food production and its availability is limited. (Yamane et al., 2001), (Van Gerpen et al., 2004), (Knothe G, 2005), (Laurikko J, 2007), (Mikkonen S, 2007), (Reinhardt et al., 2006), (Mäkinen et al., 2005) 2.3 Hydrotreated vegetable oil – HVO FAME fuel quality differences can be quite large. Therefore, there has been demand for processes that use bio-based raw materials to produce high quality diesel fuels in the scope of traditional oil refineries. New kinds of renewable diesel refi nement processes that produce large quantities of hydrocarbon-based diesel fuel have been developed. Instead of the traditional esterification, in the process any vegetable oils and animal fats are hydrotreated. The process is comparable to usual diesel fuel refinement. (Mikkonen S, 2007) The first stage of the production is the pretreatment, where impurities are removed. The actual NExBTLprocess has two parts: hydrogenation and isomerisation. The pretreated compound is continuously fed into the hydrotreatment unit. The fatty acids are hydrogenated into paraffinic hydrocarbons. The hydrogenation reaction of the fatty Figure 2. The simplified chemical production process of acid molecules and the products NExBTL. (Oja et al., 2005) can be seen in figure 2. During the hydrogenation temperature is 330-450 °C and pressure 5 MPa. Catalysts, such as NiMo/Al 2 O 3 or CoMo/ Al 2 O 3 are used. (Reinhardt et al., 2006), (Oja et al., 2005) After the hydrotreatment, the mixture of hydrocarbons is isomerised. The molecular structures of the paraffinic hydrocarbons are treated with the help of a catalyst so that the number of carbon atoms remains high and methyl branches are created in the carbon chain. The end results of the reactions are also water, propane and small amounts of carbon oxides. The isomerisation should not go too far, as the end-products cetane number would decrease. During the isomerisation phase, the temperature is about the same as in the hydtrotreatment. To stabilize the catalyst, a pressure of 3,5 - 4 MPa is used. Side products of the NExBTL production process are fuel gas, which is burned for energy, and a small amo unt of biogasoline. (Reinhardt et al., 2006), (Oja et al., 2005), (Rantanen et al., 2005), (Juva A, 2007) 3 The life cycle emissions of HVO are very small, only about 50% of traditional biodiesel production emissions. The renewability of Regulated emissions Unregulated emissions NExBTL can be verified by • NOx - 0 ... - 20 % • Aldehydes - 40 ... - 45 % radioactive C14 analysis. The • Particles - 17 ... - 30 % • Benzene - 40 ... - 45 % engines and vehicles –group at • CO - 45 ... - 55 % • PAH decrease • HC - 45 ... -55 % • Mutagens decrease VTT has made exhaust gas measurements with mixtures of NExBTL and ordinary diesel in passenger cars and buses. The measurements were made with fuels consisting of 5, 15, 20 or 85 % of biocomponent. The base fuel used fulfilled basic European requirements. The results showed emission reductions, especially with carbon monoxide and hydrocarbons. With the highest NExBTL proportion –fuels, the particle and even NOx emissions were also diminished, unlike with FAME –biodiesels. According to the measurements, the emission reductions were as can be seen in table 2. (Mäkinen et al., 2005), (Juva A, 2007), (Rantanen et al., 2005) Table 2. Emission changes when using blends of traditional diesel and NExBTL. (Mäkinen et al., 2005) The characteristics of HVO are as good as or better than with usual good quality diesel fuel, although the density of HVO is lower. With HVO, flammability is good, boiling ranges lower than with normal diesel fuel and the cold operation characteristics are adjustable. Moreover, HVO contains no aromatics or oxygen. Although the lubricities of the fuels are poor, they can be easily improved with additives. (Mäkinen et al., 2005) HVO can be used with more flexibility and without some restrictions that concern usual FAME –biodiesel. The process also makes a wider range of raw materials possible. Additionally, it enables better product optimization. NExBTL has a low cloud point, which can be adjusted from - 5 to - 28°C by severity of process conditions in order to produce either summer or winter type diesel fuel. The end product is very similar to conventional synthetic diesel fuel and can thus be blended directly with it or be sold as such to be further processed. No upper limits need to be set for HVO blends, as long as the final blend fulfills EN 590 requirements. In practice, the lower density of HVO means that the limits of EN 590 are reached with a 30% NExBTL blend. (Reinhardt et al., 2006), (Mäkinen et al., 2005), (Rantanen et al., 2005) 2.4 Fischer-Tropsch –diesels One of the most promising routes to produce liquid green fuels is the combination of biomass gasification (BG) and Fischer-Tropsch (FT) synthesis. In FT synthesis, solid or liquid raw materials are first gasified. If the synthesis gas feed is from biological masses, the end product is called BTL (“Biomass to Liquids”). Current fuel research focuses on both BTL and “gas-to-liquids” (GTL), that uses natural gas and refinery gas (“flared gas”) from petroleum production. Both concepts use synthetic gas (“syngas”, mixture of carbon monoxide and water) to produce a liquid fuel. After cleaning, the syngas is used for FT synthesis to produce long-chain hydrocarbons that are converted into “green diesel”. The syngas obtained from biomasses is termed “bio-syngas”. The process of FT synthesis using biomass feedstock is under development. (Brown D, 2007), (Boerrigter et al., 2002), (Srinivas et al., 2006) 4 The production process for BTL is started by grinding and drying of biomass, which is then formed into pellets. The biomass-pellets are diverted into a gas (smoldering gas) and solid fraction (charcoal) in a low temperature gasification process and transformed into a synthetic gas in a second step. In syngas production, the coal of the raw material is gasified by heating. The syngas mixture is formed in the presence of oxygen and water. Since the reactions are mainly exothermic and dependent on temperature, good heat transfer in the reactor is essential. An important and useful reaction is water-gas shift (WGS): (Boerrigter et al., 2002), (Srinivas et al., 2006), (Hepola et al., 2002) The syngas produced in the gasifier consists mainly of carbon monoxide (CO) and hydrogen (H2). Also small amounts of carbon dioxide and methane are in the mixture. The sulphur of the raw material is reduced to hydrogen sulfide and nitrogen to ammonia. The raw syngas mixture has to be cleaned. The most important contaminants are aromatics, ammonia and other nitrogen compounds, hydrogen sulfide and chloride and solids. The major gas cleaning issue is the tars in the gas, so a tar cracker in the system is required. Organic contaminants can be cracked or washed away. As the syngas needs to be compressed to 25-60 bar for FT synthesis, the concentration of the organic compounds must be below the dew point at FT pressure to prevent condensation and fouling in the system. Sulphuric contaminant removal is especially important, as they are harmful for the FT –synthesis catalysts. NH3 and H2 S can be removed via wet scrubbing followed by active-carbon and ZnO filters. Solids must be removed essentially completely, as they foul the system and may obstruct the fixed-bed. With respect to the other constituents of biosyngas, i.e. H2, CO, CO 2, CH 4, N2, paraffins (ethane and propane), and olefins, there are no specifications. The gas is suitable as feed for FT synthesis assuming the syngas is free of tars and other impurities. (Boerrigter et al., 2002), (Srinivas et al., 2006) After purification the gas is liquefied in the FT reaction, in which carbon monoxide (CO) and hydrogen (H) react and form carbon-hydrogen chains. In the catalytic FischerTropsch synthesis one mole of CO reacts with two moles of H 2 to form mainly aliphatic straight-chain hydrocarbons (CxHy ). Typical FT catalysts are based on iron or cobalt. About 20% of the chemical energy is released as heat in exothermic reactions that form paraffins (2), olefins (3) and alcohols (4): As follows from equations (2) – (4), the FT reaction consumes hydrogen and carbon monoxide in a ratio of H 2/CO = 2. When the ratio in the feed gas is lower, it can be adjusted with the water-gas shift (WGS) reaction (1). (Boerrigter et al., 2002), (Vessia Ø, 2005), (Cao et al., 2003) Typical operation conditions for FT synthesis, when aiming for long-chain products, are temperatures of 200-250 °C and pressures of 25-60 bar. The resulting paraffin-like liquid 5 is isomerized to achieve better cold operation and then distilled or cracked. In this step, the specifications of the fuel can be fine-tuned to match the requirements of the engines by altering the form or length of the fuel molecules. The higher the temperatures, the more short-chained hydrocarbons are formed. This fine-tuning is not possible in the currently used standard refining process for diesel or gasoline. With respect to the production of FT diesel, process conditions can be selected to produce maximum amounts of products in the diesel-range or towards production of long-chained hydrocarbons (wax). The wax can be cracked to yield predominantly diesel fuel. This hydrocracking requires additional hydrogen, for instance from a syngas side-stream that is completely shifted to hydrogen via the WGS reaction (1). Other fractions can be used in the chemical industry or be further processed. (Brown D, 2007), (Boerrigter et al., 2002), (Srinivas et al., 2006), (Lieberz S, 2004), (Hepola et al., 2002) Today, it is not yet economic to convert biomass to fuels using conventional FT technologies. Production costs are about three times as high as with traditional diesel. Commercial plant capacity, a secure feedstock supply and existing pipelines to move syngas to large central facilities are yet to be established for the BTL route. The high capital cost is a significant barrier. Energy efficiency should still be increased, it being about 45% from tree-to-barrel at the moment. (Brown D, 2007), (Srinivas et al., 2006), (Lieberz S, 2004), (Cao et al., 2003) Fischer-Tropsch diesel fuel can be produced so that it is similar to fossil diesel with regard to almost all properties, the exception being density which tends to be lower. If the relatively small density differences are not regarded, FT-diesel can be blended with fossil diesel in any proportion without the need for engine or infrastructure modifications. As FT-fuels and HVO consist of same kinds of hydrocarbons, also their characteristics are the same. FT fuel lubricity is low, and the cold operation properties depend on the production process conditions. Cetane numbers of FT-diesels are very high and aromatic contents low, which results in lower NOx and particle emissions. BTL is also CO2 – neutral as the comb ustion only releases the cola in the biomass. (Berlowitz et al., 2003) 2.5 Dimethyl ether – DME Table 3. DME compared with propane and butane. (Haikonen T, 2004) Dimethyl ether (DME, CH 3OCH 3) is structurally the simplest ether, chemically stable and colorless. Its Property DME Propane Butane qualities are most comparable with Boiling Point, °C -24,9 -42,1 -0,5 propane or butane (table 3). In Vapor Pressure @ 20 °C, bar 5,1 8,4 2,1 normal temperature and pressure Liquid Density, @ 20 °C , 668 501 610 kg/m3 DME is gaseous, having a boiling Lower Heating Value, kJ/kg 28,43 46,36 45,74 temperature of –25 °C in Auto Ignition Temperature @ 235atmospheric pressure. DME is easy 470 365 1 atm, °C 350 to liquefy by increasing pressure, Explosion/Flammability Limit 3,4since its steam pressure is 5,1 bar at 2,1-9,4 1,9-8,4 in air, vol % 17 20 °C. DME disintegrates quickly in atmosphere and isn’t carcinogenic or dangerous to the ozone layer. 6 DME can be produced by dissociating methanol into DME and water or from syngas by direct synthesis. In dissociating DME from methanol, following reactions take place: These reactions require a catalyst that is stable in high temperatures. Such are for instance nickel and zinc oxide. This so-called Topsoe process can be seen in figure 3. The process consists of desulphurization, Auto Thermal Reforming (ATR), removal of carbon dioxide, oxidation synthesis and final purification. DME is suitable for the diesel process, but it has very low viscosity (1/10 of conventional diesel fuel Figure 3. Schematic of DME production process. (Haikonen T, 2004) viscosity), lubricity, density and heating value. The compressibility of DME is three times the conventional diesel compressibility. DME requires e.g. a high-pressure injection system. Because of the low viscosity, traditional seals will leak when using DME. The viscosity can be increased with additives, but the additives deteriorate properties of the fuel. DME may also erode conventional rubber and plastic parts. The Young’s modulus of DME is very dependent on temperature, which causes problems with regular pumps, as the amount of pumped fuel decreases as temperature rises. Because of the low heating value, DME has to be injected 1,8 times as much as regular diesel for the same power. The low lubricity can be increased with additives quite easily. The high compressibility of DME causes problems with injection system as high-pressure peaks are formed in the injector after injection. Also cavitation becomes a problem. No soot is formed in DME combustion. Compared with conventional diesel, the DME spray injected into the combustion chamber mixes better with air. Therefore good combustion will take place with less air. DME combustion is quicker, late combustion phase longer and thermal efficiency better than with diesel. The emissions are lower than with diesel, if the injection system is optimized. (Berlowitz et al., 2003), (Haikonen T, 2004), (Yu et al., 2002) DME is an interesting fuel in many ways, and it has to be taken into account when assessing possibilities for future fuels. However, in this case it was estimated that the differences in the physical properties of DME and conventional diesel are very significant. At this stage it was not deemed sensible to make the needed changes to the 7 research engine EVE, especially as at the same time it should be run with other diesel fuels. Therefore, DME wasn’t part of the simulation program. 2.6 Fuel Comparison Renewable diesels have both advantages and disadvantages when compared with regular diesel. A comparison of renewable diesel raw materials, processes, and end products can be seen in table 4. FAME is a mature technology with low capital costs, but limited quality, feedstocks and views for the future, BTL technologies are very young, hindered with high costs but have much potential with large feedstocks and high quality. Hydrotreated oils fall in Table 4. Renewable diesel fuels: basic information. (Bown D. 2007) between, as the feedstocks are same with FAME, FAME HVO BTL production commercialized Process Gasification, Transesterification Hydrotreatment and the quality is as with route FT Feed BTL. The main advantage of Vegetable oils Oils, fats Biomass Product all different renewable diesel Isomerized Isomerized fuels is their reduced Product Fatty acid methyl paraffinic paraffinic (type) esters emissions. The CO2 emissions hydrocarbons hydrocarbons of FAME depend heavily on Product Consistency and High High the raw materials and their quality stability issues cultivation, and the emission 0.3-1.5 kg 0.5-1.5 kg CO2 1.6-2.3 kg CO2 /kg CO2/kg oil CO2/kg oil emissions reduction can be nonexistent. oil equivalent equivalent equivalent (LCA) BTL has at its best as high as Note: Fossil diesel fuel value reported as 3.8 kg CO2 / kg oil 90% CO2 life cycle reduction. equivalent (Vessia Ø, 2005) Although thermodynamically similar or even better than conventional diesel, renewable diesels exhibit some differences in chemistry and in such physical properties like density, viscosity and isothermal compressibility, that strongly affect injection pressure, injection rate, fuel spray characteristics, combustion characteristics and emissions. The different diesel fuel characteristics can be seen in table 5. (Yamane et al., 2001) The properties mainly affecting the functioning of the fuel injection system (not the combustion) are compressibility, density and viscosity. The boiling points don’t seem to be a problem, as they are either about the same or higher than with ordinary diesel. (Juva A, 2007), (Nylund et al., 2007) The main renewable diesel divergences from EN 590 requirements for a typical diesel fuel are lower (HVO and BTL) or higher (FAME) densities. The different densities mean that there will be differences in fuel spray. The higher the density, the higher the mass flow will be. In order to achieve the same power with low-density fuel, a larger volume of fuel per cycle should be injected. The volumetric flow should decrease with viscosity. 8 Table 5. Properties of different diesel fuels. (Juva A, 2007) Fuel NExBTL Diesel GTL FT Typical FAME Typical Standard EN 590 diesel Density at +15°C (kg/m3) Viscosity at +40°C (mm2 /s) Cetane number 10 % distillation (°C) 90 % distillation (°C) Cloud point (°C) Heating value (MJ/kg) Heating value (MJ/l) Polyaromatics (wt-%) Oxygen content (wt-%) Sulfur content (mg/kg) 780 - 785 3.0 - 3.5 98 - 99 260- 270 295 - 300 - 15 44 34,5 0 0 < 10 770- 785 3.2- 4.5 73 - 81 260 325 - 330 0 ... +3 43 33,8 0 0 < 10 885 4.5 51 340 355 0 ... - 5 38 34 0 11 < 10 835 3.5 53 200 350 -5 43 36 4 0 < 10 820-845 2.0-4.5 >51 <11 <50 Compressibility (bulk modulus) has its effect on fuel injection system functioning. For instance, because of its very compressibility, DME was left out of the simulation program and near-future plans for EVE. FAME has at low liquid pressure and temperature a bulk modulus higher than conventional diesel. When using FAME, the rate of liquid pressure rise increases and the injection timing advances with decrease in fuel temperature. Therefore, also the peak injection pressure is higher at low mean injection pressure conditions. The reason for the high biodiesel NOx emissions largely may be attributable to the difference in bulk modulus between conventional diesel fuel and biodiesel (FAME). At higher temperatures and pressures these differences in compressibility disappear. An opposite trend is observed with paraffinic fuels. Their use leads to a retarding of injection timing because they have a lower bulk modulus of compressibility. This supports the observation that paraffinic (HVO and FT-diesel) fuels yield lower NOx emissions. The conclusion is that in a high-pressure common rail system, the bulk modulus values of renewable diesels are not considered critical to the functioning of the fuel injection system. (Yamane et al., 2001), (Boehman et al., 2003) Diesel engines are not as sensitive to vapour pressure variations as SI-engines. The vapour pressures of renewable diesels are quite similar to traditional diesel. Thus, vapour pressure has not been considered an issue when using different renewable diesels. (Beer et al., 2001) The physical properties of the renewable diesel fuels don’t have many differences with conventional diesel and those deviations that do exist are relatively small. In order to make EVE research engine compatible with renewable diesels, it shouldn’t be necessary to make large-scale changes to the engine. Chemistry must be taken into account, and if FAME is to be used in large quantities, rubber parts should be changed. The density, compressibility and viscosity differences mean that the injection parameters must be optimized for each fuel to reach the best possible performance. 9 3. THE SIMULATION MODEL The one-dimensional compressible flow solution of GT-FUEL is based on a flow solution developed for 3D CFD applications (Gosman A, 1985), reduced to one dimension. An explicitly conservative finite volume solution of mass and energy is applied. (Gamma Technologies, 2003), (Seenikannan et al., 2008), (Gosman A, 1985) The GT-FUEL model (figure 4) of EVE engine was created by using 30 different templates to describe the physical parts, properties and boundary conditions of the system. The injector dimensions of were in Figure 4. Model of the injector of EVE fuel injection system. most cases gotten from Wärtsilä. The liquid diesel fuel and their gaseous forms were referenced in their own simulation objects. The simulated fuels were a typical EN 590 specifications fulfilling summer-grade diesel fuel (here “EN 590”), FAME, NExBTL, a typical Fischer-Tropsch fuel (“GTL”) and “Tempera-15”. “Tempera15” is a previously used fuel model in EVE-simulations, so it was used as a reference fuel in the test runs to fit the simulation model to real EVE measurements. To describe the properties of compressible fuels, two different equations of state for density (polynomial and “GTI”), were used. The polynomial form is often used to model fuel behavior and “GTI” is an improved power form for evaluating properties at high pressures. The “GTI” equation has been shown to yield more accurate density predictions when extrapolated to high pressures. (Kolade et al., 2003) In the “Tempera-15” –model, the fuel density was modeled with the polynomial form (8) of the density (kg/m3). In other modeled fuels the density model used was the “GTI” power form (9): where Tref = 298 K and p ref = 1 bar and T and p must be expressed in K and bar. (Kolade et al., 2003) 10 Table 5 properties were used and the density curve of the GT-FUEL reference fuel was fitted into the data. Coefficient a0 was changed so that table 5 values of fuel density at 288 K were on the curve. The fuel density curves (p = 1 bar) obtained thus can be seen in figure 5. Surprisingly, the fuel model used previously (Tempera-15) didn’t seem to fulfill EN 590 requirements, as it had a density of the same order as FAME. The density seems to fit very well with some checkpoints obtained: FAME density of 841 kg/m3 ± 2.5% at 80 °C and normal diesel density 788 kg/m3 ± 0.5% at 80 °C. (Ejima et al., 2006) The viscosities of the fuels were also obtained from table 5. In GT-FUEL the dynamic viscosity values are defined as an array, where a certain viscosity value corresponds with given temperature and pressure. Many points of reference can be given. The program interprets the viscosity to change linearly between the reference points and outside the range of the points uses the value of the nearest point. The viscosities in the different fuel models were defined based on the original GT-FUEL diesel fuel behavior. Figure 5. The simulated fuel density curves at p = 1 bar. As an example, the viscosity behavior of the fuel models at 1 bar is illustrated in figure 6. The aim of the procedure was to set the extreme condition viscosity values at a level “same or worse than in reality”. From test runs during April 2007, injection durations (in seconds), the start of injection (SOI) timings (in crank angle degrees) and corresponding injection doses were gathered for different rail pressures (1400, 1300, 1200 and 1100 bars). The needle valve was then adjusted to open accordingly at each scenario. Corresponding cylinder pressure curves were set as boundary conditions for each scenario. Figure 6. The fuel viscosity curves at 1 bar. 11 At the test simulations, after the needle valve opening arrays were set to be such that the injection timings and lengths corresponded quite well to the measurements made, the total injected masses matched relatively well the reality (figure 7). Also temperatures and pressures had to be taken into account when the simulation model accuracy and the choices made Figure 7. Simulated and measured injection doses. were evaluated. The temperatures had been evaluated to be below 400 K, remained at maximum around 360 K. The pressure peak reached as high as 1700 bar, which was judged to be normal high-pressure injector behavior. Figure 7. Simulated and measured injection doses 4. THE SIMULATION RESULTS Figure 8. The simulated mass flow rates as a function of crank angle. In the actual simulations the goal was to evaluate the compatibility of the research engine EVE and usual renewable diesels. The simulations were run with the rail pressures used in the test runs (1100, 1200, 1300 and 1400 bars), but here we concentrate on the simulations run with 1400 bar rail pressure. As the fuel behavior differences were similar, so the emphasis on the highest pressure with the most extreme values does not leave out any essential information. From the figure 8, it can be seen that the injection mass flow rates were as expected. The mass flow rate curves are shaped very typically for a common rail engine and they are very similar with the different fuel models. The magnitude of the fuel injection rates are in the order of increasing density. The flow rates naturally follow the pressure in the fuel gallery (figure 9). Right after the injection starts, the pressure drops Figure 9. Fuel gallery pressure curves in the simulations. 12 rapidly to recover again. The injection flow rates follow (the rapid decline at about 358 degrees). The injection stops as the needle valve is closed and the needle settles on its seat again blocking the injection flow. This causes a peak in the pressure at about crank angle 390 degrees. The fluctuating pressures settle to the 1400 bars of the high-pressure pump by the end of the cycle. The pressure curves of the different fuels are very similar to one another. The pressure drop between the upper fuel gallery and the volume in the upper end of the injector is essential to the functioning of the injector, since the pressure difference causes the force difference that moves the needle from its seat as the injection starts. This pressure difference caused by the opening of the needle valve between the high-pressure and the low-pressure sections of the injector can be seen in figure 10. No great differences can be seen Figure 10. The pressure drop between the fuel gallery and between the different fuels and the the volume behind the needle. injector works as expected. The needle valve acts as the actuator of the operation of the injector, as with it the pressure behind the needle is controlled (that is why it is also called “control valve”). In the rail accumulator volume, the conditions change very little, as is predictable in such a large volume (over 10:1 in relation to other parts of the fuel injection system). The rail pressure behavior can be seen in figure 11. The pressure amplitude in the rail volume is quite small, about 15 bars at maximum. Figure 11. The simulated fuel pressure curves in the rail accumulator volume. 13 5. CONCLUSIONS The examination of the simulated values and curves shows quite convincingly that the behaviors of the different renewable diesels in the fuel injection system differ only little from the behavior of conventional diesel. The greatest differences in the physical properties of the renewable diesels, when compared with conventional fuel, were the densities. However, this had little effect on the functioning of the fuel injection system in the simulations. The observation is in line with previous studies. (Ejima et al., 2006) Lower density fuels contain less energy per unit volume. This, consequently, results in a loss of engine performance in conventional high pressure injector fuel injection system engines. However, high pressure common rail fuel injection system compression ignition engines can be operated with no performance debit and with a significant reduction in emissions by using a low density diesel fuel. The fuel density should be about 0.83 g/cc or less, and the viscosity should be about 3 cSt or less at 40 o C. Viscosity seems to be more important for the fuel behavior in a diesel engine. However, it has mostly effect on the fuel spray and droplet size. (Ejima et al., 2006), (Schilowitz et al., 2002) Combined with the observation about the effect of fuel density on the performance in power, the study on the effect of the physical properties should have its emphasis on the fuel spray and the combustion in the cylinder. In the fuel injection system itself, more important factors would be the chemical properties. If FAME is used, the possible fuel injection system corrosion, and hardening or embrittlement of rubber parts must be avoided by changing seals etc. to ones made of materials that can withstand the slightly acidic fuel and/or by using only smaller fractions of FAME blended with other fuels. The low lubricity of HVO and Fischer-Tropsch fuels must be corrected with additives. An interesting possibility is to blend low -density paraffinic fuels (FT-fuels and NExBTL) with FAME and thus get an all-biofuel blend with the weaker properties of both fuels enhanced. The high density of FAME would be improved with the low density of the paraffinic diesel and vice versa, the low lubricity of the paraffinic fuels improved with FAME (that improves lubricity even in low portions), the high viscosity and boiling ranges of FAME improved with the lower ones of the paraffinic fuels and the lower heating value and cetane number of FAME improved by the higher ones of the paraffinic fuels. Paraffinic fuels could also improve FAME cold flow properties. All the fuels involved are readily biodegradable and non-toxic if spilt. Neither FAME nor the paraffinic fuels contain aromatics or sulphur, which would normally limit blending ratios with conventional diesel. More FAME (50%) could be mixed with paraffinic fuels than with conventional diesel (20%). This method has been tried and patented with GTL and conventional FAME - biodiesel. (De Boer et al., 2004) All in all, the possibilities of using biofuels in EVE research engine seem to be very good. No extensive modifications, but a possible change of seals in contact with the fuel, to the fuel injection system seem to be needed. Only the injection itself should be optimized for each fuel used, as the differences in the physical properties mostly seem to affect the fuel spray and combustion properties. 14 REFERENCES BEER T., GRANT T., MORGAN G., LAPSZEWICZ J., ANYON P., EDWARDS J., NELSON P., WATSON H., WILLIAMS D. (2001). Comparison of Transport Fuels. Final Report to the Australian Greenhouse Office on the Stage 2 study of Life-cycle Emissions Analysis of Alternative Fuels for Heavy Vehicles. EV45A/2/F3C. Australian Greenhouse Office. BERLOWITZ P., WITTENBRINK R., Cook B. (2003). Low Emissions Fischer-Tropsch Fuel/Cracked Stock Blends. European Patent EP1307529. July 5. BOEHMAN A., ALAM M., SONG J., ACHARYA R., SZYBIST J., ZELLO V., MILLER K. (2003). Fuel Formulation Effects on Diesel Fuel Injection, Combustion, Emissions and Emission Control. Proceedings of DOE 2003 Diesel Engine Emissions Reduction Conference . August 24-28, Newport, Rhode Island, USA. BOERRIGTER H., DEN UIL H., CALIS H. (2002). Green Diesel from Biomass via Fischer-Tropsch synthesis: New Insights in Gas Cleaning and Process Design. Pyrolysis and Gasification of Biomass and Waste, Expert Meeting . September 30 - October 1 2002, Strasbourg, France. BOWN D. (2007). Techno-economic evaluation of emerging biodiesel production technologies. AMEC. Ref. No. 14020075. AMEC. London. CAO C., WANG Y., HU J., ELLIOTT D., JONES S., STEVENS D. (2005). Microchannel Catalytic Process for Converting Biomass Derived Syngas to Transportation Fuels. A.C.S. symposium series. Vol. 914, pp. 273-284. DE BOER J., LAMPRECHT D. (2004) Biodiesel Fischer-Tropsch Hydrocarbon Blend. United States Patent 20040231237. November 25. EJIMA C., FLECKA B., AMIRFAZLI A. (2006) Analytical study for atomization of biodiesels and their blends in a typical injector: Surface tension and viscosity effects. ScienceDirect: Fuel. Vol. 86, pp. 15341544. GAMMA TECHNOLOGIES (2003). GT-FUEL version 6.0 user’s manual. Gamma Technologies. GOSMAN A. (1985) Multidimensional modeling of cold flows and turbulence in Reciprocating engines. SAE Paper 850344. HAIKONEN T. (2004). DME tulevaisuuden polttoaineena . Helsinki University of Technology. Internal Combustion Engine Laboratory. HEPOLA J., KURKELA E. (2002). Energiantuotannon tehostaminen fossiilisiin ja uusiutuviin polttoaineisiin pe rustuvassa energiantuotannossa. VTT Research Notes 2155. JUVA A. (2007). Neste Oilin Biopolttoaineet. handouts, Neste Oil Oyj. KNOTHE G. (2005), Dependence of biodiesel fuel properties on the structure of fatty acid alkyl esters. ScienceDirect: Fuel Processing Technology. Vol 86, pp. 1059-1070. KOLADE B., BOGHOSIAN M., REDDY P., GALLAGHER S. (2003). Development of a GeneralPurpose, Thermal-Hydraulic Software and Its Application to Fuel Injection Systems. SAE Paper 2003-010702. LAURIKKO J. (2005). Ajoneuvokalusto ja tieliikenteen energiahuolto Suomessa vuonna 2020. handouts. VTT Processes. 15 LEHTO K. (2007). Yksisylinterisen tutkimusmoottorin kampi- ja vanttiilikoneiston sekä ahtojärjestelmän simulointi. Helsinki University of Technology, Internal Combustion Engine Laboratory, 2007 LIEBERZ S. (2004). Biofuels in Germany - Prospects and limitations 2004. USDA Foreign Global Agriculture Information Network. Report Number: GM4048. MIKKONEN S. (2007). NExBTL – Second Generation Biodiesel. Handouts. Neste Oil Oyj. MIKKONEN S. (2007). Tulevaisuuden nestemäiset biopolttoaineet. Handouts. Neste Oil Oyj. MIKKONEN S., NIEMI N., ORPANA K. (2007). Polttoaineopas 2007. Neste Oil Oyj. MÄKINEN T., SIPILÄ K., NYLUND N. (2005). Liikenteen biopolttoaineiden tuotanto- ja käyttömahdollisuudet Suomessa – taustaselvitys. VTT Research Notes 2288. Valopaino Oy. Helsinki . NYLUND N., AAKKO P. (2007). Outlook for Transportation Fuels – Opportunities for high quality biofuels. Climbus yearly seminar. June 12-13. OJA S., ROUHIAINEN J. (2005). NExBTL - Renewable Synthetic Diesel. Handouts, Neste Oil Oyj. OLENIUS T. (2006). EVE Research Engine - Extreme Value Engine. Presentation. Helsinki University of Technology. Internal Combustion Engine Laboratory. RAIKO R., KURKI-SUONIO I., SAASTAMOINEN J., HUPA M. (2002) Poltto ja palaminen . Gummerus. Jyväskylä. 2. edn. ISBN 951-666-604-3. RANTANEN L., LINNAILA R., AAKKO P., HARJU T. (2005). NExBTL – Biodiesel fuel of the second generation. SAE international. 2005-01-3771. REINHARDT G., GÄRTNER S., HELMS H., RETTENMAIER N. (2006). An Assessment of Energy and Greenhouse Gases of NExBTL. Institute for Energy and Environmental Research, Heidelberg. SCHILOWITZ A., RICKEARD D., BATEMAN J., MANN N. (2002). Method for reducing emissions from high pressure common rail fuel injection diesel engines. United States Patent 20020151756, October 17. SEENIKANNAN P., PERIASAMY V., NAGARAJ P.(2008) A Design Strategy for Volumetric Efficiency Improvement in a Multi-cylinder Stationary Diesel Engine and its Validity under Transient Engine Operation. American Journal of Applied Sciences. March 2008 SRINIVAS S., MALIK R., MAHAJANI S. (2006). Fischer-Tropsch synthesis using bio-syngas and CO2. National Conference on Advances in Energy Research. December 4-5, Mumbai, India. VAN GERPEN J., SHANKS B., PRUSZKO R., CLEMENTS D., KNOTHE G. (2004). Biodiesel Production Technology: August 2002–January 2004. Technical report - National Renewable Energy Laboratory. US Dep. of Energy, Colorado. VESSIA Ø. (2005). Biofuels from lignocellulosic material - In the Norwegian context 2010 – Technology, Potential and Costs. Norwegian University of Science and Technology. Trondheim. YAMANE K., UETA A., SHIMAMOTO Y. (2001). Influence o f physical and chemical properties of biodiesel fuels on injection, combustion and exhaust emission characteristics in a direct injection compression ignition engine . International Journal of Engine Research. Vol 2. Issue 4. YU, J., LEE, J., BAE, C. (2002). Dimethyl Ether (DME) Spray Characteristics Compared to Diesel in a Common-Rail Fuel Injection System. SAE Paper, No. 2002-01-2898. 16