# Investigations on Performance and Emission Characteristics of Diesel Engine with Biodiesel (Jatropha Oil) and Its Blends

Authors: Amar Pandhare; Atul Padalkar
Journal: Journal of Renewable Energy
 (2013)

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## Abstract

This paper presents the performance of biodiesel blends in a single-cylinder water-cooled diesel engine. All experiments were carried out at constant speed 1500 rpm and the biodiesel blends were varied from B10 to B100. The engine was equipped with variable compressions ratio (VCR) mechanism. For 100% Jatropha biodiesel, the maximum fuel consumption was 15% higher than that of diesel fuel. The brake thermal efficiency for biodiesel and its blends was found to be slightly higher than that of diesel at various load conditions. The increase in specific fuel consumption ranged from 2.75% to 15% for B10 to B100 fuels. The exhaust gas temperature increased with increased biodiesel blend. The highest exhaust gas temperature observed was 430°C with biodiesel for load conditions 1.5 kW, 2.5 kW, and 3.5 kW, where as for diesel the maximum exhaust gas temperature was 440°C. The CO2 emission from the biodiesel fuelled engine was higher by 25% than diesel fuel at full load. The CO emissions were lower with Jatropha by 15%, 13%, and 13% at 1.5 kW, 2.5 kW, and 3.5 kW load conditions, respectively. The NOx emissions were higher by 16%, 19%, and 20% at 1.5 kW, 2.5 kW, and 3.5 kW than that of the diesel, respectively.


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## Body

## 1. Introduction

Diesel engines have provided power units for road transportation systems, ships, railway locomotives, equipment used for farming, construction, and in almost every type of industry due to its fuel efficiency and durability. However, Diesel engines are the major sources ofNOx and particulate matter emissions which are environmental concerns. For automotive industry the reduction of NOx and PM emission is the most important task. National governments are imposing stringent emissions on automotive sector to reduce NOx and PM emissions. Also global house warming gases (GHG) are going to receive more focus from future autosector. Therefore, the stringent emission regulation requirements give a major challenge to comply emission targets while maintaining its performance, drivability, durability, and fuel economy. The use of alternative fuels for internal combustion engines has attracted a great deal of attention due to fossil fuel crisis and also GHG impact. Alternative fuels should be easily available, environment friendly, and technoeconomically competitive. Successful alternative fuel should fulfill environmental and energy security needs without sacrificing engine operating performance [1]. Renewable resources offer the opportunity to tap local resources and reduce dependency on fossil energy resources. Most biodiesel oils, particularly of the nonedible type can be used as fuel in diesel engines. They contain significant amount of oxygen [2, 3]. The idea of using vegetable oils as fuel for diesel engine is not new. When Rudolf diesel invented diesel engine and demonstrated in the 1900 world exhibition in Paris, using peanut oil and presented that “The use of vegetable oils for engine fuels may seem insignificant today, but such oils may become in course of time as important as petroleum and coal tar products of present times” [4].One of the promising alternative fuel considered for diesel engine is biodiesel. Biodiesel fuels are renewable, as the carbon released by the burning of biodiesel fuel is used when the oil crops undergo photosynthesis. Biodiesel also offers the advantage of being able to readily use in existing diesel engines without engine modifications [5–9]. Eventhough biodiesel has many advantages, because of engine problems its use is restricted to maximum 20% only [10, 11]. Also when biodiesel is used as fuel in existing engines, there is decrease in power, drop in thermal efficiency, increase in specific fuel consumption, and higher NOx emissions [12–15]. In order to overcome these problems various modifications in engine operating parameters are suggested. The various modifications suggested are varying the compression ratio [16–18], injection pressure [19–21], use of multiple injections, oil preheating, and so forth [22–24]. Table 1 presents the comparison of properties of diesel and biodiesel (Jatropha).Table 1
Properties of diesel and Jatropha oil.
Properties
Diesel
Jatropha oil
Density (kg/m3)
840
918
Viscosity (cSt)
9.59
49.9
Calorific value (kJ/kg)
42,390
39,774
Flash point (°C)
75
240
Cetane number
45–55
45
Carbon residue (%)
0.1
0.44


## 2. Present Work

Present research work has been focused to investigate the effect of compression ratio and injection pressure on the performance, emissions, and combustion parameters of Jatropha blended fuelled engine. Experiments were conducted at different compression ratios and different injection pressures. All experiments are carried out on a single-cylinder diesel engine used for agriculture purposes and at a constant speed of 1500 rpm. The experimental results of thermal efficiency, HC, CO,NOx, smoke opacity, BP, and thermal efficiency were analyzed at various loads points of 25%, 50%, 75%, and 100%.


## 3. Experimental Setup and Experiments

A typical 3.5 kW single-cylinder 4-stroke water-cooled diesel engine at 1500 rpm was used for the research work, and Table2 presents engine specifications.Table 2
Engine specifications.
Parameter
Specifications
Engine type
4-stroke, water-cooled, single-cylinder
Bore (mm)
87.5
Stroke (mm)
110
Compression ratio
17.5 : 1
Rated power (kW)
3.5
Cooling fluid
Water
Number of cylinders
OneThe schematic diagram of the experimental set up is shown in Figure1. An eddy current dynamometer was used for load control on the engine. The piezoelectric pressure transducer was mounted on cylinder head. Various thermocouple temperature sensors were installed at appropriate locations to measure water inlet and outlet, manifold air temperature, exhaust outlet, and heat exchanger outlet temperatures. A temperature thermocouple was installed on the surface of high pressure fuel pipe. A precision crank angle encoder was coupled with the main shaft of the engine. Two openings were made in exhaust gas pipeline for sampling purposes. Fuel metering was done using a burette fitted with a three-way valve measuring unit installed on fuel tank as shown in Figure 1. The mass flow rate of intake air was measured with an orifice meter connected to a manometer. A surge tank was used to damp out the pulsations produced by the engine, for ensuring a steady flow of air through the intake manifold. An AVL 444 Di gas analyzer was used for measuring the CO, HC, and  NOx emissions and the smoke density was measured using AVL 437 smoke meter.Figure 1
The schematic diagram of the experimental setup.The engine was warmed up prior to data acquisition. All the engine test runs were carried out in fair constant ambient conditions. During the tests with Jatropha biodiesel, the engine was started with diesel until it was warmed up and then fuel was switched to various diesel-biodiesel blends. After finishing the tests with diesel-biodiesel blends, the engine was always switched back to diesel fuel and the engine was run until the biodiesel had been purged from the fuel line, injection pump, and injector. This was done to prevent starting difficulties at the later time. Initially the test engine was operated with base fuel diesel for about 10 minutes to attain the normal working temperature conditions. After that the baseline data was generated and the corresponding results were obtained.The engine was then operated with blends of Jatropha biodiesel and diesel, namely, B5, B10, B20, B40, B60, B80, and B100. At every operation the engine speed was checked and maintained constant. All the measurements were repeated five times, and the arithmetic mean of these five readings was employed for calculation and analysis. The different performance and emission parameters analyzed in the present investigation were brake thermal efficiency (BTE), brake specific fuel consumption (BSFC), exhaust gas temperature (EGT), carbon monoxide (CO), unburned hydrocarbons (UHC), nitrogen oxides (NOx), and smoke opacity. For baseline data, the engine compression ratio was set to 17.5 and fuel injection pressure (Pinj) was maintained at 180 bar. Then compression ratio was increased from 17.5 to 19.5 in the step of 1 and fuel injection pressure was varied from 180 bar to 220 bar in the step of 20 bar.


## 4. Results and Discussion

### 4.1. Emissions for Biodiesel Blends

Figure2 shows the variation in smoke opacity for all biodiesel blends at various load points. The smoke opacity was reduced in the range from 19.4% to 44.4% for various biodiesel blends as compared to that of diesel. This was mainly due to complete combustion, as additional oxygen is available from fuel itself. The smoke opacity increases with increase in engine loads. As the blend concentration was increased, smoke also increased even at lower loads and was higher than mineral diesel. This is due to poor atomization of Jatropha oil. Heavier fuel molecules, higher viscosity, and low volatility result in poor atomization of fuel. Figure 3 shows the variation in NOx emission at various load points and for various biodiesel blends. NOx  was increased in the range from 2.6% to 16.2% for various biodiesel blends for no load to full load as compared to diesel. As the engine load is increased, the mass emission of  NOx reduces. The most important factor for the formation of NOx is the combustion temperature in the cylinder and the availability of oxygen. The Jatropha oil has considerable higher viscosity which results into longer combustion duration and demonstrates significant energy release during the last phase of burning. Figures 4 and 5 show the variation of CO and THC emission trends at various loads for biodiesel blends. Continuous reduction in CO was observed at 0.5 kW, 1.5 kW, 2.5 kW load whereas at 3.5 kW load and B20 blends onwards CO emission was increased. Increase in THC emissions was noticed at full load point with increased biodiesel blends. CO emissions were reduced by 4% to 9.33% for various biodiesel blends, respectively, at full load. THC emission was reduced by 4.1% and 6.66% for B5 and B10 blends and then was increased for B20 to B100 blends. With increased Biodiesel blends, the energy content in the fuel reduces and to get same power, more quantity of fuel needs to be injected and there are chances of wall wetting and fuel trapped in crevices zones causes more THC emissions. Blends higher than 20% showed higher CO emissions than diesel fuel at high engine load. Due to higher viscosity, the air fuel mixing process is affected by the difficulty in atomization and vaporization of Jatropha oil blends. The resulting locally rich mixtures cause more incomplete combustion products such as CO and HC.Figure 2
Variation in smoke opacity for various biodiesel blends at different loads.Figure 3
Variation inNOx for various biodiesel blends at different loads.Figure 4
Variation in CO for various biodiesel blends at different loads.Figure 5
Variation in HC for various biodiesel at different loads.


### 4.2. Engine Performance for Biodiesel Blends

The engine performance indicators considered were brake specific fuel consumption (BSFC), brake thermal efficiency (Bth) and exhaust gas temperature. Figure6 shows the BSFC plots for various biodiesel fuel blends at all loads points. Brake specific fuel consumption is a measure of volumetric fuel consumption for any particulate fuel. Diesel fuel had the lowest BSFC throughout the tests. BSFC increased in the range from 2.26% to 13.58% for various biodiesel blends, respectively, than that of diesel. The increase in BSFC for the biodiesel blends may be due to biodiesels having less energy content (lower heating value) than the diesel. The higher the biodiesel content in the blend and the lower their heating values result in higher BSFC. Figure 7 shows variation in thermal efficiency for biodiesel. It was observed that for all the loads, the diesel fuel showed higher thermal efficiency as compared with blends. The thermal efficiency was decreased by 3.10% to 10.34% for various biodiesel blends, respectively, than that of diesel from no load to full load condition.Figure 6
Variation in BSFC for various biodiesel blends at different loads.Figure 7
Variation in BTE for various biodiesel blends at different loads.Figure8 shows the effect of exhaust gas temperature on diesel-biodiesel blends at 1500 rpm. The results showed that the exhaust gas temperature increased with increase in load. This is due to the poor combustion characteristics of the Jatropha curcas oil because of its high viscosity. The combustion characteristics of the blends were improved by increasing the percentage of diesel fuel in the biodiesel fuel. All the test fuels exhibited lower exhaust gas temperature as compared to diesel fuel and this phenomenon can be understood that poor BSFC can be because of poor combustion efficiency.Figure 8
Variation in EGT for various biodiesel blends at different loads.


## 4.1. Emissions for Biodiesel Blends

Figure2 shows the variation in smoke opacity for all biodiesel blends at various load points. The smoke opacity was reduced in the range from 19.4% to 44.4% for various biodiesel blends as compared to that of diesel. This was mainly due to complete combustion, as additional oxygen is available from fuel itself. The smoke opacity increases with increase in engine loads. As the blend concentration was increased, smoke also increased even at lower loads and was higher than mineral diesel. This is due to poor atomization of Jatropha oil. Heavier fuel molecules, higher viscosity, and low volatility result in poor atomization of fuel. Figure 3 shows the variation in NOx emission at various load points and for various biodiesel blends. NOx  was increased in the range from 2.6% to 16.2% for various biodiesel blends for no load to full load as compared to diesel. As the engine load is increased, the mass emission of  NOx reduces. The most important factor for the formation of NOx is the combustion temperature in the cylinder and the availability of oxygen. The Jatropha oil has considerable higher viscosity which results into longer combustion duration and demonstrates significant energy release during the last phase of burning. Figures 4 and 5 show the variation of CO and THC emission trends at various loads for biodiesel blends. Continuous reduction in CO was observed at 0.5 kW, 1.5 kW, 2.5 kW load whereas at 3.5 kW load and B20 blends onwards CO emission was increased. Increase in THC emissions was noticed at full load point with increased biodiesel blends. CO emissions were reduced by 4% to 9.33% for various biodiesel blends, respectively, at full load. THC emission was reduced by 4.1% and 6.66% for B5 and B10 blends and then was increased for B20 to B100 blends. With increased Biodiesel blends, the energy content in the fuel reduces and to get same power, more quantity of fuel needs to be injected and there are chances of wall wetting and fuel trapped in crevices zones causes more THC emissions. Blends higher than 20% showed higher CO emissions than diesel fuel at high engine load. Due to higher viscosity, the air fuel mixing process is affected by the difficulty in atomization and vaporization of Jatropha oil blends. The resulting locally rich mixtures cause more incomplete combustion products such as CO and HC.Figure 2
Variation in smoke opacity for various biodiesel blends at different loads.Figure 3
Variation inNOx for various biodiesel blends at different loads.Figure 4
Variation in CO for various biodiesel blends at different loads.Figure 5
Variation in HC for various biodiesel at different loads.


## 4.2. Engine Performance for Biodiesel Blends

The engine performance indicators considered were brake specific fuel consumption (BSFC), brake thermal efficiency (Bth) and exhaust gas temperature. Figure6 shows the BSFC plots for various biodiesel fuel blends at all loads points. Brake specific fuel consumption is a measure of volumetric fuel consumption for any particulate fuel. Diesel fuel had the lowest BSFC throughout the tests. BSFC increased in the range from 2.26% to 13.58% for various biodiesel blends, respectively, than that of diesel. The increase in BSFC for the biodiesel blends may be due to biodiesels having less energy content (lower heating value) than the diesel. The higher the biodiesel content in the blend and the lower their heating values result in higher BSFC. Figure 7 shows variation in thermal efficiency for biodiesel. It was observed that for all the loads, the diesel fuel showed higher thermal efficiency as compared with blends. The thermal efficiency was decreased by 3.10% to 10.34% for various biodiesel blends, respectively, than that of diesel from no load to full load condition.Figure 6
Variation in BSFC for various biodiesel blends at different loads.Figure 7
Variation in BTE for various biodiesel blends at different loads.Figure8 shows the effect of exhaust gas temperature on diesel-biodiesel blends at 1500 rpm. The results showed that the exhaust gas temperature increased with increase in load. This is due to the poor combustion characteristics of the Jatropha curcas oil because of its high viscosity. The combustion characteristics of the blends were improved by increasing the percentage of diesel fuel in the biodiesel fuel. All the test fuels exhibited lower exhaust gas temperature as compared to diesel fuel and this phenomenon can be understood that poor BSFC can be because of poor combustion efficiency.Figure 8
Variation in EGT for various biodiesel blends at different loads.


## 5. Variation in Compression Ratio

### 5.1. Brake Thermal Efficiency (BTE) and Brake Specific Fuel Consumption (BSFC)

Figure9 shows the effect of compression ratio for various biodiesel blends at 3.5 kW load. As the compression ratio was increased from 17.5 to 19.5 it was observed that the brake thermal efficiency increased in the range from 6.76% to 7.40% for different biodiesel blends. The increase in BTE can be attributed to reduction in heat loss and increase in power with increase in load. Figure 10 shows the variation of BSFC trend with respect to compression ratios for various biodiesel blends. The results showed that as CR increased from 17.5 to 19.5, the BSFC decreased in the range from 4.79% to 9.39% for various biodiesel blends.Figure 9
Variation in BTE for various blends at compression ratios 17.5, 18.5, and 19.5.Figure 10
Variation in BSFC for various blends at compression ratios 17.5, 18.5, and 19.5.


### 5.2. Smoke Opacity

Figure11 shows the variation of smoke opacity for various biodiesel blends of exhaust gas compared with neat diesel at different compression ratios, namely, 17.5, 18.5, and 19.5. The results showed that soot emitted by all biodiesel blends is lower than diesel at all loads and compression ratios. The reduction in smoke is observed due to combustion being mixed controlled for these blends and also the fuel bounded oxygen, as is also the case for neat diesel. For compression ratio 19.5, the reduction in smoke opacities for various blends was in the range from 19.4% to 42.8% as compared to compression ratio 17.5. The reason for this behavior was the different amount of sulphur between the diesel and biodiesel blends. Sulphur in the fuel causes formation of sulphates and increases the smoke emitted from diesel engines.Figure 11
Variation in Smoke opacity for various biodiesel blends at compression ratios 17.5, 18.5, and 19.5.


### 5.3.NOx

Figure12 shows the effect of various biodiesel blends at full load on nitric oxides (NOx). It was observed as the percentage of Jatropha oil in biodiesel increases  NOx emission increases. The Biofuels with higher oxygen contents, 1.45% to 4.075%, and neat biodiesel produce higher or a bit lower NO emissions, depending on the load. This results in lower NO formation rates since the combustion pressure rises more slowly, giving more time for cooling through heat transfer and dilution and leading to localized gas temperatures. By reducing aromatics the flame temperature will drop, leading to a lower NO production rate. As a result, the aromatics have high carbon-hydrogen ratios and thus fuels with lower aromatics will lead to a smaller amount of CO2 and larger amount of H2O being formed compared to high aromatic fuels. With further increase in blends,  NOx emissions were increased. NOx emissions varied very lightly at CR 18.5 and 19.5 and at higher biodiesel blends. At higher compression ratio  NOx is lower due to higher cetane number of the biodiesel fuel.Figure 12
Variation inNOx for various biodiesel blends at compression ratios 17.5, 18.5, and 19.5.


### 5.4. CO and THC

Figure13 shows the effect of CR on the emission of unburnt hydrocarbons (HC) and carbon monoxide (CO) for all fuels blends. Figure 13 shows CO emissions decreased by 6.94% to 10% at CR 19.5 as compared with CR 17.5 for various biodiesel blends. THC emissions decreased by 11.68% to 15.27%  at CR 19.5 as compared with CR 17.5 for various biodiesel blends. The plots showed increase in HC emissions as the quantity of diesel fuel in the blend increases.Figure 13
Variation in CO and THC for various biodiesel blends at compression ratios 17.5, 18.5, and 19.5.


## 5.1. Brake Thermal Efficiency (BTE) and Brake Specific Fuel Consumption (BSFC)

Figure9 shows the effect of compression ratio for various biodiesel blends at 3.5 kW load. As the compression ratio was increased from 17.5 to 19.5 it was observed that the brake thermal efficiency increased in the range from 6.76% to 7.40% for different biodiesel blends. The increase in BTE can be attributed to reduction in heat loss and increase in power with increase in load. Figure 10 shows the variation of BSFC trend with respect to compression ratios for various biodiesel blends. The results showed that as CR increased from 17.5 to 19.5, the BSFC decreased in the range from 4.79% to 9.39% for various biodiesel blends.Figure 9
Variation in BTE for various blends at compression ratios 17.5, 18.5, and 19.5.Figure 10
Variation in BSFC for various blends at compression ratios 17.5, 18.5, and 19.5.


## 5.2. Smoke Opacity

Figure11 shows the variation of smoke opacity for various biodiesel blends of exhaust gas compared with neat diesel at different compression ratios, namely, 17.5, 18.5, and 19.5. The results showed that soot emitted by all biodiesel blends is lower than diesel at all loads and compression ratios. The reduction in smoke is observed due to combustion being mixed controlled for these blends and also the fuel bounded oxygen, as is also the case for neat diesel. For compression ratio 19.5, the reduction in smoke opacities for various blends was in the range from 19.4% to 42.8% as compared to compression ratio 17.5. The reason for this behavior was the different amount of sulphur between the diesel and biodiesel blends. Sulphur in the fuel causes formation of sulphates and increases the smoke emitted from diesel engines.Figure 11
Variation in Smoke opacity for various biodiesel blends at compression ratios 17.5, 18.5, and 19.5.


## 5.3.NOx

Figure12 shows the effect of various biodiesel blends at full load on nitric oxides (NOx). It was observed as the percentage of Jatropha oil in biodiesel increases  NOx emission increases. The Biofuels with higher oxygen contents, 1.45% to 4.075%, and neat biodiesel produce higher or a bit lower NO emissions, depending on the load. This results in lower NO formation rates since the combustion pressure rises more slowly, giving more time for cooling through heat transfer and dilution and leading to localized gas temperatures. By reducing aromatics the flame temperature will drop, leading to a lower NO production rate. As a result, the aromatics have high carbon-hydrogen ratios and thus fuels with lower aromatics will lead to a smaller amount of CO2 and larger amount of H2O being formed compared to high aromatic fuels. With further increase in blends,  NOx emissions were increased. NOx emissions varied very lightly at CR 18.5 and 19.5 and at higher biodiesel blends. At higher compression ratio  NOx is lower due to higher cetane number of the biodiesel fuel.Figure 12
Variation inNOx for various biodiesel blends at compression ratios 17.5, 18.5, and 19.5.


## 5.4. CO and THC

Figure13 shows the effect of CR on the emission of unburnt hydrocarbons (HC) and carbon monoxide (CO) for all fuels blends. Figure 13 shows CO emissions decreased by 6.94% to 10% at CR 19.5 as compared with CR 17.5 for various biodiesel blends. THC emissions decreased by 11.68% to 15.27%  at CR 19.5 as compared with CR 17.5 for various biodiesel blends. The plots showed increase in HC emissions as the quantity of diesel fuel in the blend increases.Figure 13
Variation in CO and THC for various biodiesel blends at compression ratios 17.5, 18.5, and 19.5.


## 6. Variation in Injection Pressure

Among several combustion parameters, fuel injection pressure is one of the important parameters which has significant role on the performance and emissions of a diesel engine. Higher injection pressures generate faster combustion rates, resulting in high cylinder gas temperatures and fuel atomization characteristics improve with higher injection pressure so that higher surface area is exposed to the surrounding air. Detailed experimental work has been carried out to analyze the emission and performance characteristics of a single cylinder 3.5 kW, compression ignition engine fuelled with neat diesel and biodiesel blends at fuel injection pressures of 180 bar, 200 bar, and 220 bar. The tests were conducted at power 0.5 kW, 1.5 kW, 2.5 kW, and 3.5 kW at constant speed. The compression ratio was adjusted to 19.5 since better engine performance was observed. The brake thermal Efficiency and brake specific fuel consumption (BSFC) are calculated and the emissions measured were carbon monoxide (CO), carbon dioxide(CO2), hydrocarbon (HC), and oxides of nitrogen (NOx). Complete measurements were taken after stabilization of all operating condition at every measurement point.


### 6.1. Smoke Opacity

Smoke opacity was studied at various injection pressures and biodiesel blends at entire operating load region at constant speed 1500 rpm. Atomization characteristics are better at higher injection pressure which improves the air-fuel interaction. This phenomenon leads to improvement in combustion which resulted in lower exhaust smoke emissions. Figures14, 15, and 16 shows the effect of different fuel injection pressures 180 bar, 200 bar and 220 bar, respectively, on smoke opacity from 0.5 kW load to 3.5 kW full load, respectively. It can be concluded from the results that the smoke opacity reduced with increased injection pressures which minimizes diffusion combustion. As compared to neat diesel, smoke opacity improved by 34.7% at full load when operated at 180 bar. The improvement in smoke opacity at part load region is 15 to 20% only. Continuous improvement in smoke opacity was noticed with increased blends at Pinj=180 bar. At  Pinj=200 bar and  Pinj=220 bar injection pressures, the reduction in smoke opacity was only 10% to 15% through the load regions compared to neat diesel and 100% biodiesel blend, but there was an improvement at all pressure levels with increased blends. The main reason for reduction in smoke opacity at higher blends is that the increased oxygen percentage promotes the better combustion.Figure 14
Variation in smoke opacity for various biodiesel blends atPinj 180 bar and CR 19.5.Figure 15
Variation in smoke opacity for various biodiesel blends atPinj 200 bar and CR 19.5.Figure 16
Variation in smoke opacity for various biodiesel blends atPinj 200 bar and CR 19.5.


### 6.2. Emissions

#### 6.2.1.NOx Emissions

Figures17, 18 and 19 shows the variation of NOx emissions with different blend ratio at various load point for different Injector Opening Pressure (IOP) on research engine. NOx emissions are increasing with increase in blend ratios for all the IOP and engine load due to increase in combustion chamber temperature. As expected NOx level increases with increase in IOP due to faster combustion and higher temperature reached in the cycle in research. It was also observed that the NOx emissions rise was only by 3% at low load and full load point with all biodiesel blends. But at 1.5 kW and 2.5 kW load points, the increase in NOx was in the range from 4% to 6%. Increase in NOx emissions was observed with increased blends and load with all IOP conditions. This phenomenon was mainly due to increased in-cylinder temperature with IOP. For diesel, NOx emissions increased from 0.4% to 1.4% when operated at 180 bar, 200 bar, and 220 bar injection pressures. It may be due to active combustion caused by smaller particles of atomized fuel. Similarly NOx increased from 0.55% to 1.16% when operated from 180 bar to 220 bar injection pressure for various biodiesel blends.Figure 17
Variation inNOx for various biodiesel blends at Pinj 180 bar and CR 19.5.Figure 18
Variation inNOx for various biodiesel blends at Pinj 200 bar and CR 19.5.Figure 19
Variation inNOx for various biodiesel blends at Pinj 220 bar and CR 19.5.


#### 6.2.2. CO and THC Emissions

Figures20, 21, and 22 show the variation of THC and CO emissions with different IOPs of neat diesel, biodiesel blend fuel at 3.5 kW with IOPs of 180 bar, 200 bar and 220 bar. Unburnt hydrocarbons are results of incomplete combustion of fuel. With the injector opening pressure 180 bar, the UBHC and CO emissions are exceedingly higher compared to 200 bar, and 220 bar. This may be attributed to the incomplete and improper mixture formation of the fuel at lower injection pressure. However, with IOP 220 bar, the B20 fuel showed significant reduction in UBHC emissions. The improved performance was observed at IOP 220 bar with B20 fuel, though they reasonably have high viscosity and lower cetane number. At lower load CO emissions were found higher for all diesel-biodiesel fuel blends at different higher injection pressures, as shown in figure. This may be due to incomplete combustion at lower loads. For diesel, CO emissions increased from 7.1% to 11.4% when operated at 180 bar, 200 bar, and 220 bar injection pressures. Similarly CO emission increased from 7.25% to 34.88% when operated from 180 bar to 220 bar injection pressure for various biodiesel blends.Figure 20
Variation in CO for various biodiesel blends atPinj 180 bar and CR 19.5.Figure 21
Variation in CO for various biodiesel blends atPinj 200 bar and CR 19.5.Figure 22
Variation in CO for various biodiesel blends atPinj 220 bar and CR 19.5.


#### 6.2.3. BSFC

Figures23, 24, and 25 illustrate the variation of BSFC with different IOPs of neat diesel and at various biodiesel blends fuel over entire operating range of speed 1500 rpm. Diesel-biodiesel fuel blends were tested in the engine at 180 bar, 200 bar, and 220 bar fuel injection pressures. BSFC for biodiesel-diesel blends is higher than that of diesel at a particular injection pressure. This is due to the fact that biodiesel has lower heating value compared to diesel, so more biodiesel is needed to maintain constant power output. It can be seen that at higher injection pressure BSFC goes on decreasing. The BSFC for B100 fuels is higher than diesel and blend B20 fuel which was observed due to lower calorific values, higher density, and lower energy content. Higher the density more will be the discharge of fuel for the same displacement of the plunger of the fuel injection pump. For the injector opening pressure of 200 bar with blend B20 fuel, the BSFC of compression ignition engine for the entire load range was lower compared to other injector opening pressures. This may be due to the increased penetration length and spray cone angle and due to more area coverage of spray formed in the combustion chamber and utilizing the air effectively resulting optimum peak pressure, better fuel air mixing, and higher spray atomization. However, injector opening pressure 220 bar, the performance has suffered significantly because of low penetration and low momentum of fuel droplets. It was observed that at retard injection timing, the BSEC of B100, B20, and diesel fuel was higher than other injection timings under all the load conditions. This may be due to poor and untimely combustion fuels. But at advance injection timing, the BSEC was lower for B20 fuel than B100 and diesel fuel. This may be due to complete combustion of fuel due to sufficient duration.Figure 23
Variation in BSFC for various biodiesel blends atPinj 180 bar and CR 19.5.Figure 24
Variation in BSFC for various biodiesel blends atPinj 200 bar and CR 19.5.Figure 25
Variation in BSFC for various biodiesel blends atPinj 220 bar and CR 19.5.


### 6.3. Brake Thermal Efficiency

Figures26, 27, and 28 illustrate the variation of brake thermal efficiency (BTE) with different IOPs with neat diesel and biodiesel blend fuel at various load points and at speed 1500 rpm. It is observed that efficiency obtained at full load and part load of blend B20 fuel with injector opening pressure 220 bar is higher than the B100 and diesel fuel compared with other injector opening pressures and similar increase in the thermal efficiency was also observed in the remaining loads. It can be observed that the thermal efficiency of all fuels at lower injection pressure is low due to coarse spray formation and poor atomization and mixture formation of biodiesel during injection. However, with higher injection opening pressure due to the fine spray formed during injection and improved atomization, resulted with lower physical delay period yielding in better combustion. This will enhance combustion and in turn improves efficiency. For blend B20 fuel, the brake thermal efficiency is markedly higher than B100 fuel and diesel fuel. The possible reason for the above findings is attributed to the additional lubricity of biodiesel which tends to minimize the frictional losses in the cylinder. The maximum BTE occurred with IOP 220 bar and blend B20 which was selected as optimal injection pressure. Further, increase in the injector opening pressure beyond 220 bar to 240 bar resulted in decrease in the thermal efficiency with all test fuels. This may be due to the fact that at higher injection opening pressure, the size of fuel droplets decreases drastically. It can be observed that the brake thermal efficiency for biodiesel is lower than diesel fuel. This is because of lower heating value and specific gravity. The combination of heating value and mass flow rate indicates energy input to the engine. This energy input or consumption to the engine in case of biodiesel is more compared to diesel. It has been also observed that as the injection pressure goes on increasing brake thermal efficiency also goes on increasing over all the range of biodiesels.Figure 26
Variation in BTE for various biodiesel blends atPinj 180 bar and CR 19.5.Figure 27
Variation in BTE for various biodiesel blends atPinj 200 bar and CR 19.5.Figure 28
Variation in BTE for various biodiesel blends atPinj 180 bar and CR 19.5.


## 6.1. Smoke Opacity

Smoke opacity was studied at various injection pressures and biodiesel blends at entire operating load region at constant speed 1500 rpm. Atomization characteristics are better at higher injection pressure which improves the air-fuel interaction. This phenomenon leads to improvement in combustion which resulted in lower exhaust smoke emissions. Figures14, 15, and 16 shows the effect of different fuel injection pressures 180 bar, 200 bar and 220 bar, respectively, on smoke opacity from 0.5 kW load to 3.5 kW full load, respectively. It can be concluded from the results that the smoke opacity reduced with increased injection pressures which minimizes diffusion combustion. As compared to neat diesel, smoke opacity improved by 34.7% at full load when operated at 180 bar. The improvement in smoke opacity at part load region is 15 to 20% only. Continuous improvement in smoke opacity was noticed with increased blends at Pinj=180 bar. At  Pinj=200 bar and  Pinj=220 bar injection pressures, the reduction in smoke opacity was only 10% to 15% through the load regions compared to neat diesel and 100% biodiesel blend, but there was an improvement at all pressure levels with increased blends. The main reason for reduction in smoke opacity at higher blends is that the increased oxygen percentage promotes the better combustion.Figure 14
Variation in smoke opacity for various biodiesel blends atPinj 180 bar and CR 19.5.Figure 15
Variation in smoke opacity for various biodiesel blends atPinj 200 bar and CR 19.5.Figure 16
Variation in smoke opacity for various biodiesel blends atPinj 200 bar and CR 19.5.


## 6.2. Emissions

### 6.2.1.NOx Emissions

Figures17, 18 and 19 shows the variation of NOx emissions with different blend ratio at various load point for different Injector Opening Pressure (IOP) on research engine. NOx emissions are increasing with increase in blend ratios for all the IOP and engine load due to increase in combustion chamber temperature. As expected NOx level increases with increase in IOP due to faster combustion and higher temperature reached in the cycle in research. It was also observed that the NOx emissions rise was only by 3% at low load and full load point with all biodiesel blends. But at 1.5 kW and 2.5 kW load points, the increase in NOx was in the range from 4% to 6%. Increase in NOx emissions was observed with increased blends and load with all IOP conditions. This phenomenon was mainly due to increased in-cylinder temperature with IOP. For diesel, NOx emissions increased from 0.4% to 1.4% when operated at 180 bar, 200 bar, and 220 bar injection pressures. It may be due to active combustion caused by smaller particles of atomized fuel. Similarly NOx increased from 0.55% to 1.16% when operated from 180 bar to 220 bar injection pressure for various biodiesel blends.Figure 17
Variation inNOx for various biodiesel blends at Pinj 180 bar and CR 19.5.Figure 18
Variation inNOx for various biodiesel blends at Pinj 200 bar and CR 19.5.Figure 19
Variation inNOx for various biodiesel blends at Pinj 220 bar and CR 19.5.


### 6.2.2. CO and THC Emissions

Figures20, 21, and 22 show the variation of THC and CO emissions with different IOPs of neat diesel, biodiesel blend fuel at 3.5 kW with IOPs of 180 bar, 200 bar and 220 bar. Unburnt hydrocarbons are results of incomplete combustion of fuel. With the injector opening pressure 180 bar, the UBHC and CO emissions are exceedingly higher compared to 200 bar, and 220 bar. This may be attributed to the incomplete and improper mixture formation of the fuel at lower injection pressure. However, with IOP 220 bar, the B20 fuel showed significant reduction in UBHC emissions. The improved performance was observed at IOP 220 bar with B20 fuel, though they reasonably have high viscosity and lower cetane number. At lower load CO emissions were found higher for all diesel-biodiesel fuel blends at different higher injection pressures, as shown in figure. This may be due to incomplete combustion at lower loads. For diesel, CO emissions increased from 7.1% to 11.4% when operated at 180 bar, 200 bar, and 220 bar injection pressures. Similarly CO emission increased from 7.25% to 34.88% when operated from 180 bar to 220 bar injection pressure for various biodiesel blends.Figure 20
Variation in CO for various biodiesel blends atPinj 180 bar and CR 19.5.Figure 21
Variation in CO for various biodiesel blends atPinj 200 bar and CR 19.5.Figure 22
Variation in CO for various biodiesel blends atPinj 220 bar and CR 19.5.


### 6.2.3. BSFC

Figures23, 24, and 25 illustrate the variation of BSFC with different IOPs of neat diesel and at various biodiesel blends fuel over entire operating range of speed 1500 rpm. Diesel-biodiesel fuel blends were tested in the engine at 180 bar, 200 bar, and 220 bar fuel injection pressures. BSFC for biodiesel-diesel blends is higher than that of diesel at a particular injection pressure. This is due to the fact that biodiesel has lower heating value compared to diesel, so more biodiesel is needed to maintain constant power output. It can be seen that at higher injection pressure BSFC goes on decreasing. The BSFC for B100 fuels is higher than diesel and blend B20 fuel which was observed due to lower calorific values, higher density, and lower energy content. Higher the density more will be the discharge of fuel for the same displacement of the plunger of the fuel injection pump. For the injector opening pressure of 200 bar with blend B20 fuel, the BSFC of compression ignition engine for the entire load range was lower compared to other injector opening pressures. This may be due to the increased penetration length and spray cone angle and due to more area coverage of spray formed in the combustion chamber and utilizing the air effectively resulting optimum peak pressure, better fuel air mixing, and higher spray atomization. However, injector opening pressure 220 bar, the performance has suffered significantly because of low penetration and low momentum of fuel droplets. It was observed that at retard injection timing, the BSEC of B100, B20, and diesel fuel was higher than other injection timings under all the load conditions. This may be due to poor and untimely combustion fuels. But at advance injection timing, the BSEC was lower for B20 fuel than B100 and diesel fuel. This may be due to complete combustion of fuel due to sufficient duration.Figure 23
Variation in BSFC for various biodiesel blends atPinj 180 bar and CR 19.5.Figure 24
Variation in BSFC for various biodiesel blends atPinj 200 bar and CR 19.5.Figure 25
Variation in BSFC for various biodiesel blends atPinj 220 bar and CR 19.5.


## 6.2.1.NOx Emissions

Figures17, 18 and 19 shows the variation of NOx emissions with different blend ratio at various load point for different Injector Opening Pressure (IOP) on research engine. NOx emissions are increasing with increase in blend ratios for all the IOP and engine load due to increase in combustion chamber temperature. As expected NOx level increases with increase in IOP due to faster combustion and higher temperature reached in the cycle in research. It was also observed that the NOx emissions rise was only by 3% at low load and full load point with all biodiesel blends. But at 1.5 kW and 2.5 kW load points, the increase in NOx was in the range from 4% to 6%. Increase in NOx emissions was observed with increased blends and load with all IOP conditions. This phenomenon was mainly due to increased in-cylinder temperature with IOP. For diesel, NOx emissions increased from 0.4% to 1.4% when operated at 180 bar, 200 bar, and 220 bar injection pressures. It may be due to active combustion caused by smaller particles of atomized fuel. Similarly NOx increased from 0.55% to 1.16% when operated from 180 bar to 220 bar injection pressure for various biodiesel blends.Figure 17
Variation inNOx for various biodiesel blends at Pinj 180 bar and CR 19.5.Figure 18
Variation inNOx for various biodiesel blends at Pinj 200 bar and CR 19.5.Figure 19
Variation inNOx for various biodiesel blends at Pinj 220 bar and CR 19.5.


## 6.2.2. CO and THC Emissions

Figures20, 21, and 22 show the variation of THC and CO emissions with different IOPs of neat diesel, biodiesel blend fuel at 3.5 kW with IOPs of 180 bar, 200 bar and 220 bar. Unburnt hydrocarbons are results of incomplete combustion of fuel. With the injector opening pressure 180 bar, the UBHC and CO emissions are exceedingly higher compared to 200 bar, and 220 bar. This may be attributed to the incomplete and improper mixture formation of the fuel at lower injection pressure. However, with IOP 220 bar, the B20 fuel showed significant reduction in UBHC emissions. The improved performance was observed at IOP 220 bar with B20 fuel, though they reasonably have high viscosity and lower cetane number. At lower load CO emissions were found higher for all diesel-biodiesel fuel blends at different higher injection pressures, as shown in figure. This may be due to incomplete combustion at lower loads. For diesel, CO emissions increased from 7.1% to 11.4% when operated at 180 bar, 200 bar, and 220 bar injection pressures. Similarly CO emission increased from 7.25% to 34.88% when operated from 180 bar to 220 bar injection pressure for various biodiesel blends.Figure 20
Variation in CO for various biodiesel blends atPinj 180 bar and CR 19.5.Figure 21
Variation in CO for various biodiesel blends atPinj 200 bar and CR 19.5.Figure 22
Variation in CO for various biodiesel blends atPinj 220 bar and CR 19.5.


## 6.2.3. BSFC

Figures23, 24, and 25 illustrate the variation of BSFC with different IOPs of neat diesel and at various biodiesel blends fuel over entire operating range of speed 1500 rpm. Diesel-biodiesel fuel blends were tested in the engine at 180 bar, 200 bar, and 220 bar fuel injection pressures. BSFC for biodiesel-diesel blends is higher than that of diesel at a particular injection pressure. This is due to the fact that biodiesel has lower heating value compared to diesel, so more biodiesel is needed to maintain constant power output. It can be seen that at higher injection pressure BSFC goes on decreasing. The BSFC for B100 fuels is higher than diesel and blend B20 fuel which was observed due to lower calorific values, higher density, and lower energy content. Higher the density more will be the discharge of fuel for the same displacement of the plunger of the fuel injection pump. For the injector opening pressure of 200 bar with blend B20 fuel, the BSFC of compression ignition engine for the entire load range was lower compared to other injector opening pressures. This may be due to the increased penetration length and spray cone angle and due to more area coverage of spray formed in the combustion chamber and utilizing the air effectively resulting optimum peak pressure, better fuel air mixing, and higher spray atomization. However, injector opening pressure 220 bar, the performance has suffered significantly because of low penetration and low momentum of fuel droplets. It was observed that at retard injection timing, the BSEC of B100, B20, and diesel fuel was higher than other injection timings under all the load conditions. This may be due to poor and untimely combustion fuels. But at advance injection timing, the BSEC was lower for B20 fuel than B100 and diesel fuel. This may be due to complete combustion of fuel due to sufficient duration.Figure 23
Variation in BSFC for various biodiesel blends atPinj 180 bar and CR 19.5.Figure 24
Variation in BSFC for various biodiesel blends atPinj 200 bar and CR 19.5.Figure 25
Variation in BSFC for various biodiesel blends atPinj 220 bar and CR 19.5.


## 6.3. Brake Thermal Efficiency

Figures26, 27, and 28 illustrate the variation of brake thermal efficiency (BTE) with different IOPs with neat diesel and biodiesel blend fuel at various load points and at speed 1500 rpm. It is observed that efficiency obtained at full load and part load of blend B20 fuel with injector opening pressure 220 bar is higher than the B100 and diesel fuel compared with other injector opening pressures and similar increase in the thermal efficiency was also observed in the remaining loads. It can be observed that the thermal efficiency of all fuels at lower injection pressure is low due to coarse spray formation and poor atomization and mixture formation of biodiesel during injection. However, with higher injection opening pressure due to the fine spray formed during injection and improved atomization, resulted with lower physical delay period yielding in better combustion. This will enhance combustion and in turn improves efficiency. For blend B20 fuel, the brake thermal efficiency is markedly higher than B100 fuel and diesel fuel. The possible reason for the above findings is attributed to the additional lubricity of biodiesel which tends to minimize the frictional losses in the cylinder. The maximum BTE occurred with IOP 220 bar and blend B20 which was selected as optimal injection pressure. Further, increase in the injector opening pressure beyond 220 bar to 240 bar resulted in decrease in the thermal efficiency with all test fuels. This may be due to the fact that at higher injection opening pressure, the size of fuel droplets decreases drastically. It can be observed that the brake thermal efficiency for biodiesel is lower than diesel fuel. This is because of lower heating value and specific gravity. The combination of heating value and mass flow rate indicates energy input to the engine. This energy input or consumption to the engine in case of biodiesel is more compared to diesel. It has been also observed that as the injection pressure goes on increasing brake thermal efficiency also goes on increasing over all the range of biodiesels.Figure 26
Variation in BTE for various biodiesel blends atPinj 180 bar and CR 19.5.Figure 27
Variation in BTE for various biodiesel blends atPinj 200 bar and CR 19.5.Figure 28
Variation in BTE for various biodiesel blends atPinj 180 bar and CR 19.5.


## 7. Conclusions

From the experimental investigations on use of Jatropha biodiesel blend in a single-cylinder diesel engine, the following conclusions could be drawn. Single-cylinder diesel engine requires no modification in hardware during testing. The effect of compression ratios for various blends of B5, B10, B20, B40, B60, B80, and B100 has been concluded.(i)
Improvement in BTE and BSFC was observed at higher compressions ratio 19.5 as compared to 17.5 at all blends. It showed that the higher compression ratio compensate the loss of BTE with biodiesel blends. The brake thermal efficiency was found to increase with increase in compression ratio and there is no significant difference in the brake thermal efficiency of biodiesel blends and neat diesel. However BTE increased in the range from 6.76% to 7.40% for different biodiesel blends.(ii)
Low smoke opacity was observed with higher compression ratio due to better combustion. Maximum reduction in smoke opacity was 22% at compression ratio 19.5.(iii)
The CO and THC emissions decreased by 7 to 10% with CR 19.5 as compared with CR 17.5 at all biodiesel blend ratios. The biodiesel fuel has high viscosity, so due to high viscosity the air-fuel mixing process is affected by the difficulty in vaporization and atomization. The resulting rich mixtures causes incomplete combustion because of lack of oxygen content and produces higher emissions.(iv)
Diesel-biodiesel fuel blends were tested in the engine at 180 bar, 200 bar, and 220 bar fuel injection pressures. BSFC for biodiesel-diesel blends is higher than that of diesel at a particular injection pressure. This is due to the fact that biodiesel has lower heating value compared to diesel, so more biodiesel is needed to maintain constant power output. It can be seen that at higher injection pressure BSFC goes on decreasing.(v)
Continuous improvement in smoke opacity was noticed with increased blends atPinj=180 bar. At Pinj=200 bar and  Pinj=220 bar injection pressures, the reduction in smoke opacity was only 10 to 15% through the load regions as compared to neat diesel and 100% biodiesel blend, but there was an improvement at all pressure levels with increased blends. The main reason for reduction in opacity at higher blends due to increased oxygen percentage promotes the better combustion.(vi)
HigherNOx emissions by 1.4% were observed at 220 bar as compared to 180 bar. At lower load CO emissions were found higher for all diesel-biodiesel fuel blends at different higher injection pressures. Mainly due to incomplete combustion at lower loads points with higher air fuel ratio promote cool combustion. However maximum  NOx emission increased with the mass percent of oxygen in the biodiesel.(vii)
Overall combustion characteristics for all blends were found similar to diesel at all compression ratios. Peak pressure increases with increase in compression ratios for all biodiesel blends and neat diesel. At CR 19.5, ignition delay is shorter for all biodiesel blends than neat diesel due to higher cetane number.(viii)
Biodiesel blends have more heat release rate than mineral diesel at CR 19.5. Diesel fuel shows lowest heat release rate initially and longer duration.(ix)
Peak pressure increases with increase in loads for all fuels and at all compression ratios. Blends have more peak pressure than neat diesel and at higher compression ratio and it decreases as the biodiesel percentage decreases.(x)
A practical conclusion can be drawn that all tested fuel blends can be used safely without any modification in engine. So blends of methyl esters of Jatropha oil could be used successfully.(xi)
On the whole it is concluded that Jatropha oil can be used as fuel in diesel engine directly and by blending it with diesel fuel. Use of Jatropha oil can give better performance and reduced smoke emissions.



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*Source: 163829-2013-03-14.xml*