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Attempts to reduce biodiesel blends N[O.sub.x] pollutant emissions by ultrasonic conditioning.

Introduction

It is widely accepted that biodiesel is one of the current solutions in an attempt to limit the effect of Internal Combustion (IC) engines greenhouse emissions.

The pollution caused by nitric oxides emissions is capable to forming a variety of cytotoxic species, which contribute to lung pathology and disease, with implication in pathogenesis of acute respiratory distress syndrome (Sunil et al. 2009).

Nabi and Hustad (2010) and Zhu et al. (2010) showed that in case of biodiesel use for fueling diesel engine, emissions of N[O.sub.x] increase by 2/4% (for B20 blend) as much 12/20% (for B100). The biodiesel N[O.sub.x] specific increase effect is related to the differences in physico-chemically characteristics (viscosity, density, bulk modulus of compressibility, bond structure, and cetane number), fuel injection timing and spray char acteristics, and engine operation condition, with major influences on the combustion process (Mazzoleni et al. 2007; Knothe 2008).

The differences between the physical properties of methyl ester based biodiesel and diesels are major and some are presented in Table 1. These differences lead to difficulties in using biodiesel in high blends (> 30%) with diesel fuel in existing compression ignition engines (Kegl et al. 2008; Park et al. 2009; Payri et al. 2011).

One way to improve the physical parameters of biodiesel (to reduce the pollutant emissions) is to use external energy transfer irradiation with different sources (ultrasound, microwaves, infrared waves, ultraviolet, etc.). Some of these energy sources are able to modify at the micro molecular level the chemical structure of the biodiesel, with immediate influence on its physical properties (Stavarache et al. 2006; Dzida, Prusakiewicz 2008; Lee et al. 2011). Ultrasonic irradiation is able to make these changes due to the phenomenon of cavitation, which takes place through the interaction of ultrasound waves with the molecular structure of the biodiesel (Kang et al. 2001; Stavarache et al. 2006; Wu et al. 2007).

The models proposed by Kang et al. (2001) and Mason and Lorimer (1989, 2002), explain the kinetics of chemical transformations whereby the action of external energy influences the cavitation process at the molecular level. The models describe how through the process of ultrasonic irradiation conditioning and characteristics such as high local pressure and temperature, substances undergo chemical reactions in two main directions:

--pyrolysis-type chemical reactions--the transformation mechanism is decisive in the development of a chemical high-intensity thermal effect (local temperature can reach 5000 K) at the molecular level;

--a multiphase chemical reaction in the formation of radicals.

Availability (affinity) of hydroxyl compounds formed in the process of irradiation and combined (being in excess in the mechanism of chemical reactions) leads to the formation of peroxides. Peroxide formations of these groups increases the efficiency of fuel combustion process, with beneficial influences on the further development of thermal processes in the functional cycle of an internal combustion engine, as well as providing changes in the biodiesel's physical properties.

The amount of peroxide formed depends directly on the intensity and duration of the ultrasonic irradiation process (Mariasiu et al. 2009; Lee et al. 2011).

1. Material and Methods

1.1. Laboratory Experiments

The aim of the research was to provide a primary image of the processes taking place during the ultrasonic irradiation of biodiesel. Was used experimental methods and methodologies employed (and validated) by other researchers. For the sound of speed measurement we used the proposed methodology of Dzida and Prusakiewicz (2008), and for determining the intensity of the ultrasonic waves we took into account the experiments carried out by Wu et al. (2007) and Gogate and Kabadi (2009). Also taken into account were the related observations made by other researchers (Tat, Van Gerpen 2003a; Payri et al. 2011).

The biodiesel chosen for experimentation was Rapeseed Methyl Ester (RME), mainly used in Europe. The samples of vegetable oil-based biofuels blended with diesel fuel used as the subject for the experiments had the following composition:

--fuel sample control - diesel (diesel fuel);

--fuel 1 - B25 (75% diesel fuel + 25% rapeseed oil methylester);

--fuel 2 - B50 (50%diesel fuel + 50% rapeseed oil methylester);

--fuel 3 - B75 (25% diesel fuel + 75% rapeseed oil methylester);

--fuel 4 - B100 (100% rapeseed oil methylester).

The BXXUs_irr abbreviation was used for the ultrasonic irradiated biodiesel blends (where XX represents the volumetric percentage of methyl ester in the blends with the diesel fuel). The initial properties of the biodiesel were determined in laboratory conditions and are presented in Table 2. The variants of the physical parameters on which the experiments were focused, were the density (determined by Anton Paar 5000 apparatus), the speed of sound passing through the medium (Optel measuring device) and the viscosity (Haake viscometer). The isentropic bulk modulus of the biofuels conditioned by irradiation with ultrasound was determined by using the Newton-Laplace formula (Tat, Van Gerpen 2003b; Dzida, Prusakiewicz 2008):

[beta] = [rho] x [u.sup.2], (1)

where: [beta] is the isentropic bulk modulus [Pa]; u is the speed of sound [m/s]; [rho] is density of the sample [kg/[m.sup.3]].

Determination of the isentropic bulk modulus value is significant in measuring the effect of ultrasonic irradiation on the process of ignition and combustion of conditioned biofuels. This is because the isentropic bulk modulus value influences the injection time. Furthermore, Tat and Van Gerpen (2003a), Szybist et al. (2005, 2007) and Bakeas et al. (2011) noted that a higher value of isentropic bulk modulus corresponded to higher N[O.sub.x] values. The experiments conducted by Boehman et al. (2004), Torres-Jimenez et al. (2011) confirm totally or partially this hypothesis.

Ultrasound propagation in vegetable oil and also in biofuel causes cavitation (under specific conditions). Because of the expansion and contraction of the transfer media are conditions to generate locally bubbles of very high temperature and of pressure (cavitation process). As an immediate result, the physical and chemical properties of the transfer media are modified (Stavarache et al. 2006).

Gogate and Kabadi (2009) show that the effectiveness (efficiency) of the ultrasonic horn in creating a cavitation effect depends on the magnitude of energy and operating frequency supplied by the equipment. It was observed that the cavitation intensity decreases exponentially until it vanishes completely at a distance of as low as 20-50 mm from the ultrasonic horn. To create the cavitation phenomenon in the ultrasonic irradiation of biofuels for the present experiment, we used a small volume of biofuel for conditioning ([V.sub.BD] = 300 ml) and an ultrasonic horn that produces 35 W/L, PZT type, at 35 kHz frequency emission, which was applied continuously. Measurements of physical properties considered in the experiments were carried out after a duration of ultrasonic irradiation of 0, 100, 200, 300, 400, 500 and 600 seconds and were compared with the values of the same physical properties of diesel fuel that was not irradiated (sample control).The energy density transferred to the biofuel volume was analyzed by the method proposed and used by Ramirez-Del-Solar et al. (1990) and Lee et al. (2011).

The ultrasonic power was calculated from:

[P.sub.us] = [E.sub.us]/t, (2)

where: [P.sub.us] is ultrasonic power [W]; [E.sub.us] is ultrasonic energy [J]; t is time [seconds].

The [P.sub.us] is constant (from the installation construction) and therefore the energy density can be calculated using (Lee et al. 2011):

[U.sub.us] = [P.sub.us] x [t/[V.sub.BD]], (3)

where: [V.sub.DB] is the volume of irradiated biofuel (biodiesel) [ml].

For the experimental conditions described above, the values of the transferred ultrasonic energy density in biodiesel blends are presented in Table 3.

Moreover, the ultrasonic conditioning process gives rise to conditions where peroxide compounds might form (as oxidation mechanism of Fatty Acid Methyl Ester - FAME), resulting in a beneficial influence on fuel combustion, but this may also have negative influence on the storage properties of the biodiesel (especially in the long term).

1.2. Test Bed Experiments

To determine the influence of the instantaneous ultrasonic irradiation process on biodiesel with regard to N[O.sub.x] emission, we used an experimental test bed equipped, developed and adjusted in accordance with the methodology of the research in the field (Szybist et al. 2007; Kegl et al. 2008).

The experiments were carried out to determine the differences between the emission of N[O.sub.x], for irradiated and non-irradiated biodiesel (compared with the same values for diesel fuel) using an engine experimental test bed, presented in Fig. 1.

The constructive details of vessel use to ultrasonic conditioning the biodiesel blends (patent pending) are presented in Fig. 2. The engine was run at constant speed of 2400 min-1, and a Weinlich M 8000 dynamometer was also use to load the engine. The loads at 25, 50, 75 and 100% correspond to 0.10, 0.20, 0.31 respectively 0.41 MPa of Brake Mean Effective Pressure (BMEP).

The structural parameters and functional characteristics of the Yanmar diesel engine L 100 AE used in the experiments are presented in Table 4.

The experimental test was performed examining the full range of engine load. The N[O.sub.x] emissions were measured with a Testo 330 XL exhaust gas analyzer (with N[O.sub.x] measurement cell). The calibration procedure for the gas analyzer was done before each test (in accordance with the manufacturer's recommendations in order to achieve measurements errors of less than 2%). The experimental tests were performed 10 times, and the results of those repetitions were averaged to reduce the level of uncertainty.

[FIGURE 1 OMITTED]

[FIGURE 2 OMITTED]

2. Results and Discussion

The biodiesel parameters considered for determining the influence of the ultrasonic irradiation process were: speed of sound through the medium, density, isentropic bulk modulus and kinematic viscosity. The results obtained from the experiments are presented in Figs 3-6 (laboratory tests) and Figs 7-10 (engine test bed experiments).

As the duration of treatment increased, the overall trend for the speed of sound variation among the ultrasonic irradiated blends was downward (Fig. 3). After 600 seconds of irradiation, all values (except for B100Us_irr) were equal or smaller than the value for the diesel fuel speed of sound.

The induced thermal effect caused by the ultrasounds interaction with the conditioned volume of blends was measured, to determine the magnitude of the induced temperature on biodiesel blends physical parameters characteristics.

[FIGURE 3 OMITTED]

[FIGURE 4 OMITTED]

[FIGURE 5 OMITTED]

[FIGURE 6 OMITTED]

The variation is linear with the time; a slope of 2.15 [degrees]C/min, 2.21 [degrees]C/min, 2.36 [degrees]C/min and 2.44 [degrees]C/min was measured for the B25, B50, B75 and respectively for B100 blend. The maximum temperature was achieve for B100 blend (42.4 [degrees]C after 600 seconds of ultrasonic conditioning; initial biodiesel blends temperature was 18 [degrees]C), but according to the experiments effectuated by Bari et al. (2002), a temperature of the fuel less than 60 [degrees]C, did not have a significant effect on the fuel consumption and effective power.

For a period of approximately 420 seconds of ultrasonic irradiation conditioning, the density of biodiesel B25Us_irr density fell below that of the diesel fuel (Fig. 4). For the other blends (B50, B75 and B100) the density decreased by an average value of 2.49 %, but the final values were higher than those of the diesel fuel. The effect of density decreasing is beneficial regarding the fuel injection process, with immediate consequences for the pollutant emission levels (Park et al. 2009).

In general, the trend of the isentropic bulk modulus variation was decreasing, with a minimum value of 4.71% (B100Us_irr) and a maximum of 9.68% (B25Us_ irr) (Fig. 5). Isentropic bulk modulus values dropped below those of the diesel fuel mixture for B25Us_irr (after 100 seconds) and B50Us_irr (after 350 seconds) blends. Szybist et al. (2005, 2007) and Bakeas et al. (2011) show that higher bulk modulus causes advanced injection timing, one of the reasons for increased N[O.sub.x] pollutant emissions. From the point of view of the presented experiments, the decreasing tendency of the isentropic bulk modulus for all the blends shows possibilities for reduced N[O.sub.x] emissions from biodiesel-fueled engines. The variation of isentropic bulk modulus has direct effect on biodiesel's ignition timing (that are more appropriate in conditions of ultrasonic irradiation to diesel fuel one). Further, from this reason, the peak combustion temperature in the N[O.sub.x] formation interval is decrease, because the premixed combustion intensity is reduced (Wang et al. 2007).

Only B25Us_irr blend's kinematic viscosity shows lower values than those of diesel fuel in the process of ultrasonic irradiation (after 350 seconds). The difference between the kinematic viscosity of the B25Us_irr blend subjected to the full irradiation time of 600 seconds and that of the diesel fuel after 600 seconds was 28.25% (Fig. 6). Ultrasonic irradiation was also beneficial for the other considered blends (B50, B75 and B100): kinematic viscosity was reduced by an average of 19.74%. Viscosity is considered a more important biodiesel parameter that density, owing to its direct influence on the operation of fuel injection engines' equipment (Mariasiu et al. 2009). Szybist et al. (2005) highlight the beneficial effect of a fuel with lower viscosity on injection process parameters. Furthermore, the effect is related to reduced N[O.sub.x] emissions.

The results obtained in experiments to test the fueling of a DI diesel engine with ultrasonically irradiated biodiesel confirm the interpretation of previous assumptions about biodiesels' physical parameter changes under the effects of ultrasonic irradiation. The generally decreasing tendency of the treated biodiesels' density, viscosity and isentropic bulk modulus brings beneficial effects to the injection and combustion processes, with a direct influence on N[O.sub.x] pollutant emissions formation.

According to the results presented in Figs 7-10, there are reductions in N[O.sub.x] pollutant emissions for all regimes of the engine. The maximum value obtained is 18.2% (for B25Us_irr, no engine load case) and the minimum is 1.4% (for B100Us_irr, 100% engine load case), compared with emissions from untreated basic biodiesel. Using the ultrasonically irradiated biodiesel, reductions in N[O.sub.x] emissions of greater than 10% were obtained for low and medium load engine regimes. For B25Us_irr these load regimes are 0% and 75% (-18.2% and -11.9%); for B50Us_irr they are between 0% and 50% (-14.3% and -11.1%); and for B75Us_irr, they are for 0% engine load regime only (-10.7%).

[FIGURE 7 OMITTED]

[FIGURE 8 OMITTED]

[FIGURE 9 OMITTED]

[FIGURE 10 OMITTED]

To be able to judge the real effect of biodiesel blends ultrasonic irradiation process on N[O.sub.x] pollutant emission level, were analyzed also the engine's Break Specific Fuel Consumption (BSFC) and the brake power variations. The results are presented in Figs 11 and 12, considering the relative variation of measurements before and after ultrasonic conditioning of biodiesel blends.

From above presented results it can said that the effect of ultrasonic irradiation conduct to a generally (but smaller as values) decreasing tendency of BSFC. The major reduction in BSFC was achieve for the B100Us_irr blend equal to 2.95% (at 0% engine load). In the case of effective brake power a increasing tendency was measured with major influence on B75Us_irr and B100Us_irr blends (4.28% at 0% engine load, respectively 4.43% at 75% engine load).

Based on the presented results, it can say that the reduction of N[O.sub.x] pollutant emission is major caused by the effect of ultrasonic biodiesel blends conditioning on the isentropic bulk modulus parameters change. The decreasing in BSFC correlated with a small increasing of engine's effective power, are the immediate effect of a more appropriate ignition timing (that are influenced by the value of isentropic bulk modulus) of ultrasonic biodiesel conditioned, to that of diesel fuel.

[FIGURE 11 OMITTED]

[FIGURE 12 OMITTED]

However, the N[O.sub.x] pollutant emission values, using the ultrasonic irradiated biodiesel to fuel a DI diesel engine, remain higher than that using diesel fuel.

Conclusions

The ultrasonic irradiation process leads to important variations in the physical parameters of biodiesels. In terms of density and viscosity (important parameters for the injection process) the obtained results show equal values for the B25 blend and diesel fuel for an ultrasonic irradiation period of 420 seconds and 350 seconds respectively. The variations of ultrasonically irradiated biodiesel physical characteristics show potential in N[O.sub.x] pollutant emission reduction: potential confirmed through experimental bench research on the performance of a direct injection diesel engine.

The major reduction in N[O.sub.x] pollutant emissions was observed for the B25Us_irr blend conditioned by ultrasonic irradiation (18.2% for no engine load to 8% for 100% engine load) when compared to basic untreated biodiesel. However, there were still N[O.sub.x] emissions values greater than those measured from the diesel fuel and the biodiesel's conditioning process by ultrasonic irradiation worse storage properties for long periods (by increasing oxidative products in blends).

The results obtained can be improved through future research of the ultrasonic irradiation process on different types of methyl esters (soy, palm oil, sun flower, etc.) and with different values of transmitted ultrasonic density in fuel (taking into consideration the use of low-power and also low-cost ultrasonic horns).

Through the ultrasonic irradiation process it is feasible to incorporate biodiesel fuels into blends (with diesel fuel) for use in compression ignition engines without having to make major or important changes and adjustments to the fuel injection systems of these engines.

Caption: Fig. 1. Experimental test bed structure: 1 - fuel tank; 2 - pollutant emissions analyzer; 3 - injector; 4 - exhaust pipe; 5 - data acquisition system; 6 - engine speed sensor; 7 - single cylinder engine; 8 - air intake pipe; 9 - injection pump; 10 - ultrasonic irradiation device; 11 - fuel filter

Caption: Fig. 2. Constructive details of conditioning device: 1 - fuel-out pipe; 2 - vessel; 3 - cap; 4 - fuel-in pipe; 5 - ultrasonic emitter

Caption: Fig. 3. The influence of the ultrasonic irradiation process on the speed of sound through the medium

Caption: Fig. 4. The influence of the ultrasonic irradiation process on the density

Caption: Fig. 5. The influence of the ultrasonic irradiation process on the isentropic bulk modulus

Caption: Fig. 6. The influence of the ultrasonic irradiation process on the kinematic viscosity

Caption: Fig. 7. N[O.sub.x] emissions for the B25 blend (ultrasonic irradiated and basic biodiesel)

Caption: Fig. 8. N[O.sub.x] emissions for the B50 blend (ultrasonic irradiated and basic biodiesel)

Caption: Fig. 9. N[O.sub.x] emissions for the B75 blend (ultrasonic irradiated and basic biodiesel)

Caption: Fig. 10. N[O.sub.x] emissions for the B100 blend (ultrasonic irradiated and basic biodiesel)

Caption: Fig. 11. Differences in BSFC for non-irradiated and irradiated biodiesel blends

Caption: Fig. 12. Differences of engine's brake power for non-irradiated and irradiated biodiesel blends

Acknowledgements

This work was supported by CNCSIS-UEFISCSU, project number PNII-IDEI 175/2008.

Submitted 16 January 2012; accepted 28 March 2012

References

Bakeas, E.; Karavalakis, G.; Stournas, S. 2011. Biodiesel emissions profile in modern diesel vehicles. Part 1: Effect of biodiesel origin on the criteria emissions, Science of The Total Environment 409(9): 1670-1676. http://dx.doi.org/10.1016/j.scitotenv.2011.01.024

Bari, S.; Lim, T. H.; Yu, C. W. 2002. Effects of preheating of crude palm oil (CPO) on injection system, performance and emission of a diesel engine, Renewable Energy 27(3): 339-351. http://dx.doi.org/10.1016/S0960-1481(02)00010-1

Boehman, A. L.; Morris, D.; Szybist, J. P. 2004. The impact of the bulk modulus of diesel fuels on fuel injection timing, Energy & Fuels 18(6): 1877-1882. http://dx.doi.org/10.1021/ef049880j

Directive 2009/28/EC of the European Parliament and of the Council of 23 April 2009 on the Promotion of the Use of Energy from Renewable Sources and Amending and Subsequently Repealing Directives 2001/77/EC and 2003/30/EC. 47 p. Available from Internet: http://eur-lex.europa.eu/LexUriServ/LexUriServ.do?uri=Oj:L:2009:140:0016:0062:en:PDF

Dzida, M.; Prusakiewicz, P. 2008. The effect of temperature and pressure on the physicochemical properties of petroleum diesel oil and biodiesel fuel, Fuel 87(10-11): 1941-1948. http://dx.doi.org/10.1016/j.fuel.2007.10.010

Gogate, P. R.; Kabadi, A. M. 2009. A review of applications of cavitation in biochemical engineering/biotechnology, Biochemical Engineering Journal 44(1): 60-72. http://dx.doi.org/10.1016/j.bej.2008.10.006

Kang, J.-W.; Lee, K.-H.; Koh, C.-I.; Nam, S.-N. 2001. The kinetics of the sonochemical process for the destruction of aliphatic and aromatic hydrocarbons, Korean Journal of Chemical Engineering 18(3): 336-341.http://dx.doi.org/10.1007/BF02699174

Kegl, B.; Kegl, M.; Pehan, S. 2008. Optimization of a fuel injection system for diesel and biodiesel usage, Energy & Fuel 22(2): 1046-1054. http://dx.doi.org/10.1021/ef700657g

Knothe, G. 2008. "Designer" biodiesel: optimizing fatty ester composition to improve fuel properties, Energy & Fuels 22(2): 1358-1364. http://dx.doi.org/10.1021/ef700639e

Lee, S. B.; Lee, J. D.; Hong, I. K. 2011. Ultrasonic energy effect on vegetable oil based biodiesel synthetic process, Journal of Industrial and Engineering Chemistry 17(1): 138-143. http://dx.doi.org/10.1016/j.jiec.2010.12.012

Mariasiu, F.; Burnete, N.; Deac, T. 2009. Possibilities to determinate the biofuels physically parameters in functional conditions, Research Journal of Agricultural Science 41(2): 451-456.

Mason, T. J.; Lorimer, J. P. 2002. Applied Sonochemistry: The Uses of Power Ultrasound in Chemistry and Processing. Wiley-VCH. 314 p.

Mason, T. J.; Lorimer, J. P. 1989. Sonochemistry: Theory, Applications and Uses of Ultrasound in Chemistry. Prentice Hall. 580 p.

Mazzoleni, C.; Kuhns, H. D.; Moosmuller, H.; Witt, J.; Nussbaum, N. J.; Chang, M.-C. O.; Parthasarathy, G.; Nathago undenpalayam, S. K. K.; Nikolich, G.; Watson, J. G. 2007. A case study of real-world tailpipe emissions for school buses using a 20% biodiesel blend, Science of The Total Environment 385(1-3): 146-159. http://dx.doi.org/10.1016/j.scitotenv.2007.06.018

Nabi, M. N.; Hustad, J. E. 2010. Experimental investigation of engine emissions with marine gas oil-oxygenate blends, Science of The Total Environment 408(16): 3231-3239. http://dx.doi.org/10.1016/j.scitotenv.2010.03.043

Park, S. H.; Kim, H. J.; Suh, H. K.; Lee, C. S. 2009. Experimental and numerical analysis of spray-atomization characteristics of biodiesel fuel in various fuel and ambient temperatures conditions, International Journal of Heat and Fluid Flow 30(5): 960-970. http://dx.doi.org/10.1016/j.ijheatfluidflow.2009.04.003

Payri, R.; Salvador, F. J.; Gimeno, J.; Bracho, G. 2011. The effect of temperature and pressure on thermodynamic properties of diesel and biodiesel fuels, Fuel 90(3): 1172-1180. http://dx.doi.org/10.1016/j.fuel.2010.11.015

Ramirez-Del-Solar, M.; De la Rosa-Fox, N.; Esquivias, L. 1990. Kinetic study of gelation of solventless alkoxide-water mixtures, Journal of Non-Crystalline Solids 121(1-3): 40-44. http://dx.doi.org/10.1016/0022-3093(90)90101-Q

Stavarache, C.; Vinatoru, M.; Maeda, Y. 2006. Ultrasonic versus silent methylation of vegetable oils, Ultrasonics Sonochemistry 13(5): 401-407.

http://dx.doi.org/10.1016/j.ultsonch.2005.08.001 Sunil, V. R.; Patel, K. J.; Mainelis, G.; Turpin, B. J.; Ridgely, S.;

Laumbach, R. J.; Kipen, H. M.; Nazarenko, Y.; Veleepa rambil, M.; Gow, A. J.; Laskin, J. D.; Laskin, D. L. 2009.

Pulmonary effects of inhaled diesel exhaust in aged mice, Toxicology and Applied Pharmacology 241(3): 283-293. http://dx.doi.org/10.1016/j.taap.2009.08.025

Szybist, J. P.; Boehman, A. L.; Taylor, J. D.; McCormick, R. L. 2005. Evaluation of formulation strategies to eliminate the biodiesel N[O.sub.x] effect, Fuel Processing Technology 86(10): 1109-1126. http://dx.doi.org/10.1016/j.fuproc.2004.11.006

Szybist, J. P.; Song, J.; Alam, M.; Boehman, A. L. 2007. Bio diesel combustion, emissions and emission control, Fuel Processing Technology 88(7): 679-691. http://dx.doi.org/10.1016/j.fuproc.2006.12.008

Tat, M. E.; Van Gerpen, J. H. 2003a. Measurement of Biodiesel Speed of Sound and its Impact on Injection Timing. Subcontractor Report NREL/SR-510-31462. National Renewable

Energy Laboratory. 120 p. Available from Internet: http:// www.nrel.gov/docs/fy03osti/31462.pdf

Tat, M. E.; Van Gerpen, J. H. 2003b. Effect of temperature and pressure on the speed of sound and isentropic bulk modulus of mixtures of biodiesel and diesel fuel, Journal of the American Oil Chemists' Society 80(11): 1127-1130. http://dx.doi.org/10.1007/s11746-003-0830-x

Torres-Jimenez, E.; Dorado, M. P.; Kegl, B. 2011. Experimental investigation on injection characteristics of bioethanol-diesel fuel and bioethanol-biodiesel blends, Fuel 90(5): 19681979. http://dx.doi.org/10.1016/j.fuel.2010.11.042

Wang, D.; Zhang, C.; Wang, Y. 2007. A numerical study of multiple fuel injection strategies for N[O.sub.x] reduction from DI diesel engines, International Journal of Green Energy 4(4): 453-470. http://dx.doi.org/10.1080/15435070701465912

Wu, P.; Yang, Y.; Colucci, J.; Grulke, E. A. 2007. Effect of ultra-sonication on droplet size in biodiesel mixtures, Journal of the American Oil Chemists' Society 84(9): 877-884. http://dx.doi.org/10.1007/s11746-007-1114-9

Zhu, L.; Cheung, C. S.; Zhang, W. G.; Huang, Z. 2010. Emissions characteristics of a diesel engine operating on biodiesel and biodiesel blended with ethanol and methanol, Science of the Total Environment 408(4): 914-921. http://dx.doi.org/10.1016/j.scitotenv.2009.10.078

Florin Mariasiu

Dept of Automotive Engineering and Transports, Technical University of Cluj-Napoca, Romania

Corresponding author: Florin Mariasiu

E-mail: florin.mariasiu@auto.utcluj.ro
Table 1. Physical properties of some methylesters (Mariasiu et
al. 2009)

Fuel               Density at       Kinematic      Cetane
                 15 [degrees]C     viscosity at
                 [kg/[m.sup.3]]   40 [degrees]C
                                  [mm/[s.sup.2]]

Diesel fuel           841              2.7          54.1
Rapeseed oil          882              4.60         52.7
  methyl ester
Soybean oil           865              4.08         46.4
  methyl ester
Sunflower oil         883              4.16         49.2
  methyl ester
Olive oil             881              4.18         59.8
  methyl ester

Fuel                Cloud          Flash
                    point          point
                 [[degrees]C]   [[degrees]C]

Diesel fuel          -14             64
Rapeseed oil          1             181
  methyl ester
Soybean oil           -1            168
  methyl ester
Sunflower oil         2             178
  methyl ester
Olive oil             -2            182
  methyl ester

Table 2. Physico-chemical characteristics of the tested fuels

Property                       Diesel        Rapeseed Methyl
                                fuel           Ester (RME)

Chemical formula             [C.sub.14]   [C.sub.16]-[C.sub.18]
                             [H.sub.30]
Molecular weight [g/mol]       198.4              209.6
Density at 20 [degrees]C        831                879
  [kg/[m.sup.3]]
Kinematic viscosity at          2.7                4.9
  40 [degrees]C
  [[mm.sup.2]/s]
Boiling point [[degrees]C]      278                322
Higher heating value           46.94              37.5
  [MJ/kg]
Carbon content [%]               87               78.7
Sulphur content [ppm]           233               0.036
Water content [mg/kg]            64                86
Cetane number                   54.1              52.7

Table 3. Biodiesel blends' physical characteristics after
600 seconds of irradiation process

Blend      Density       Mean heat     Ultrasonic
        [g/[cm.sup.3]]   capacity    energy density
                          [J/gK]         [kJ/L]

B25         0.836          1.958         3519.3
B50         0.853          1.978         3931.3
B75         0.862          1.981         4166.6
B100        0.876          1.993         4521.8

Table 4. Technical characteristics of the test engine

Parameter                              Value

Type                       4-stroke, air cooled,
                             vertical single cylinder
Bore x Stroke              86x70 mm
Displacement               406 [cm.sup.3]
Combustion type            direct injection
Continuous rating output   6.6 kW at 3600 [min.sup.-1]
Fuel injection pressure    19.6 MPa
Fuel injection timing      17 [+ or -] 0.5[degrees] BTDC
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Date:Mar 1, 2014
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