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IJRET: International Journal of Research in Engineering and Technology eISSN: 2319-1163 | pISSN: 2321-7308
__________________________________________________________________________________________
Volume: 02 Issue: 12 | Dec-2013, Available @ http://www.ijret.org 46
INVESTIGATION ON EVAPORATIVE EMISSION FROM A GASOLINE
POLYCARBONATE FUEL TANK
S. Ajit1
, Thirumalini.S2
1
Master of Technology Automotive, 2
Professor, Department of Mechanical Engineering, Amrita School of Engineering
ajitnair90@gmail.com
Abstract
It is estimated that about 15 to 20 percent of the vehicle hydrocarbon (HC) emission were due to evaporation of fuel. Hence a need
was felt to understand the extent of evaporative emission from gasoline fuel system. A polycarbonate fuel tank that is predominantly
used in two wheeled vehicles is considered for study. Emission can surface to atmosphere in three modes; diffusion through fuel tank
wall, escaping through vent in tank and when fuel tank cap is opened for refueling. The average temperature condition which prevails
in south India which is in the range of 27o
C to 34o
C was considered. From which temperatures which were at proximity to peak high
and low day time were chosen. The complete set up was placed in open atmosphere to replicate the working environment. The
emission constituents and its levels were measured by conducting the test particularly for averaged out day time high and low
temperature condition. Further diffusion test was conducted within a range of 34o
C to 36o
C, this temperature is considered to be
range of maximum temperature which prevails in south India. From which a temperature was chosen and the test was conducted.
This comparative study gives an indication of emission and its quantity from the fuel tank at the ambient temperature.
Keywords: Evaporative Emission, Fuel Tank, HC Emission
----------------------------------------------------------------------***-----------------------------------------------------------------------
1. INTRODUCTION
Emission from the tail pipe is always considered the major
cause of concern, where by evaporative emissions are ignored.
Diurnal emissions are a type of evaporative emission that
originate from the vehicle fuel tank as the fuel vaporizes due to
the daily ambient temperature variations [1]
. Two wheeled
vehicles occupy a larger space on Indian roads [2]
.Diurnal
emissions are prevalent in the polycarbonate fuel tank which is
commonly used in two wheeled vehicles. These were not
sensitive to fuel tank capacity or vehicle refuelling system
geometry or configuration [3]
.Hence it is a surface phenomenon.
This emission has become a cause for concern as fuel can
evaporate from the tank which goes in to the atmosphere and
reacts with air to form harmful pollutants. Under Indian
condition where the vehicle is commonly parked in an open
space are more prone to this type of Diurnal emission. Emission
rate increases with both surrounding temperature and fuel
volatility [4]
. Evaporation led to permeation of fuel through fuel
tank walls and escaped through vent which reached the outer
environment. Fuel can also escape to atmosphere, when the fuel
tank cap is open for refuelling. When the dispensed fuel
temperature was higher than the fuel tank temperature, vapour
growth occurred [3]
.
Permeation can be checked by heating up the fuel from 15.6o
C
to 28.9o
C (60–84 F) within a period of 1 h as prescribed by the
United States Environmental Protection Agency (US
Environmental Protection Agency, 1991, 1992, 1994) and
CONCAVE (CONCAWE, 1987, 1988, 1990)[1]
. The tests were
performed using a mini-SHED, which is a structure designed to
enclose a fuel-tank instead of the entire vehicle [5]
. Experiments
were performed such that the quantities of emission
constituents were measured and a comparative study was done
for various temperatures.
2. EXPERIMENTATION PROCEDURE
During this experiment, a poly carbonate fuel tank of capacity
5000cc was used. The maximum exposed surface area to air, in
tank, occurred at capacity of 1000cc of gasoline. Hence 1000cc
of fuel was considered for study.
2.1 Permeability Test of Fuel Tank
The fuel tank was placed in a mini SHED, at ambient condition.
As shown in Fig: 1 emission gas analyzer probe was introduced
in the sealed chamber in order to measure the constituents of
emission and its quantity. This tank had a capacity to retain
heat, there by accelerated the experimental condition. Initially
the ambient temperature and temperature inside the air-tight
tank is measured. The whole set up is kept in an open
environment and the constituents are measured in time steps of
10 minutes. This emission variation along with time is plotted
and that gives a clear picture of time varying scale of emission
constituents.
IJRET: International Journal of Research in Engineering and Technology eISSN: 2319-1163 | pISSN: 2321-7308
__________________________________________________________________________________________
Volume: 02 Issue: 12 | Dec-2013, Available @ http://www.ijret.org 47
Fig: 1 Permeability Test on Fuel Tank
2.2 Break out Fuel Test
The ambient temperature is noted, as it must be correlated with
the averaged maximum or minimum day time temperature
which prevails in south India (11.0183° N, 76.9725° E). In this
test, the fuel tank was placed in the open environment for 30
minutes as shown in Fig: 2, in order to reach a thermodynamic
equilibrium. Hence this in turn will increase the temperature of
fuel inside. After 30 minutes of time the fuel tank cap is open
and thus the fuel escaped was measured with emission gas
analyzer. The analyzer indicates the value of the emission
constituents which escaped while opening cap of the fuel
tank.The probe was kept at a distance of 1 cm from the opening
of the fuel tank. The dilute fuel vapour will be sensed by the
probe which indicates the actual condition of the fuel in
atmosphere.
Fig: 2 Break Out Fuel Test
3. RESULT AND DISCUSSION
3.1 Break-Out Fuel Test at 29.8o
c
The maximum surface area was considered, for the ideal case.
The fuel had a surface area of 263.4 cm2 which is in contact
with air. HC vapour's presence was more when in compare with
NO, which is indicated as in Fig 3 and 4.
During the initial 30 minutes of tank's exposure to environment.
The ambient temperature increased the kinetic energy of the top
layer of liquid fuel particles such that it escaped the liquid
boundary and attained gaseous state. After which the
temperature of the liquid fuel reduced as the heat was carried
away by the gaseous particles. This heated the surrounding air
of gaseous particles thereby made nitrogen and oxygen which
were the components of air present in tank, to react with each
other. Thus this produced NO.
When the tank cap was opened after 30 minutes, the vapour
pressure of the fuel tried to equalize with atmospheric pressure.
Hence vapour in the form of HC and NO shot up. This dipped
as it matched with atmospheric pressure.
Fig: 3 NO Vs Time at 29.8
o
C
Fig: 4 HC Vs Time at 29.8
o
C
3.2 Break-Out Fuel Test at 34o
c
The kinetic energy of top level of fluid increased with the
increase in ambient temperature and hence the occurrence of
NO and HC vapours were high at 34o
C. This vapour
accumulated inside the tank in the initial 30 minutes of
experiment, when the fuel tank was kept in open space. After
30 minutes the fuel tank cap is opened to allow the fuel vapour
to escape out of the tank, during which the measurement of the
emission is made, which gave a plot as in the Fig 5 and 6.From
0
10
20
30
40
0 10 20 30 40NOinPPM
Time in Minutes
0
1000
2000
3000
4000
5000
0 10 20 30 40
HCinPPM
Time in Minutes
IJRET: International Journal of Research in Engineering and Technology eISSN: 2319-1163 | pISSN: 2321-7308
__________________________________________________________________________________________
Volume: 02 Issue: 12 | Dec-2013, Available @ http://www.ijret.org 48
both the breakout fuel test with different ambient temperatures
showed noticeable increase in the emissions level.
Fig 5 HC Vs Time at 34
o
C
Fig 6 d NO Vs Time at 34
o
C
3.3 Emission Due to Diffusion
The diffusion of the fuel through the fuel tank membrane was
checked at 32o
C by using a mini SHED. During this experiment
it was evident that the HC vapour emitted through the vent and
percolated through the fuel tank walls. The HC content
gradually went up to a point and then decreases as shown in Fig
7 .But the presence of NO which is visible from Fig 8 was very
low, such that it is neglected. This is because the fuel in fuel
tank is cooled by evaporative cooling and it starts cooling the
surrounding. As it is place in SHED, confined domain,
evaporative cooling effect reduced mechanism of NO
formation.
Fig 7 HC Vs Time at 32o
C
This experiment was conducted for about 50 minutes, as per the
EPA norms. The emission thus got was only for a stipulated
time. It may vary according to the quantity of exposure to heat
and time for which the tank is exposed.
Fig 8 NO Vs Time at 32o
C
CONCLUSIONS
From the result obtained, it was evident that the occurrence of
evaporative emission increased with the increase in the ambient
temperature condition. This experiment gives a clear picture of
impact of environmental temperature effects by ignoring the
temperature occurring (ex:engine) from the vehicle. The
constituent like HC was predominant in the beginning and it
gradually decreased at the end. Certain other constituents like
CO CO2 and NO were found only at higher temperatures.
It also stressed the need for eliminating the emission from the
fuel tank through vent in the tank and due to diffusion through
the fuel tank walls. However this emission might vary based on
the climatic topography of the region.
0
500
1000
1500
2000
2500
3000
3500
4000
0 10 20 30 40
HCinPPM
Time(Min)
0
20
40
60
80
100
120
0 10 20 30 40
NOinPPM
Time (Min)
0
200
400
600
800
1000
1200
1400
1600
1800
2000
0 20 40 60
HCinPPM
TIME(min)
-1
0
1
2
3
4
5
6
0 20 40 60
NOinPPM
Time (min)
IJRET: International Journal of Research in Engineering and Technology eISSN: 2319-1163 | pISSN: 2321-7308
__________________________________________________________________________________________
Volume: 02 Issue: 12 | Dec-2013, Available @ http://www.ijret.org 49
REFERENCES
[1] H. Van der Westhuisen et al 2004 “Evaluation of
evaporative emissions from gasoline powered motor
vehicles under South African conditions”, Elsevier
Atmospheric environment Vol 38 pp 2
[2] Indian Road Transport Year Book 2010- 2011
[3] Braddock, J. N., Gabele, P. A., and Lemmons, T. J.,(1986)
“Factors Influencing the Composition and Quantity of
Passenger Car Refueling Emissions – Part 1,” SAE Paper
861558.
[4] Smith, M., (1972) “An Investigation of Passenger Car
Refueling Losses,” SAE Paper 720931
[5] Giorgos Mellios et al 2009, “A vehicle testing
programme for calibration and validation of an
evaporative emissions model” Elsevier fuel pp 2
[6] United States Environmental Protection Agency, (2001)
“Evaluating Resting Loss and Diurnal Evaporative
Emissions Using RTD Tests,” Assessment and Modeling
Division,EPA420-R-01-018, M6.EVP.001, Ann Arbor,
MI.
[7] Reuter, R.M., Benson, J.D., Brooks, D.J., Dunker, A.M.,
Gorse, R.A. Jr, and Koehl, W.J., (1994) “Sources of
Vehicle Emissions in Three Day Diurnal SHED Tests –
Auto/Oil Air Quality Improvement Research Program,”
SAE Paper 941965.
[8] Furey, R., and Nagel, B., (1986) “Composition of Vapor
Emitted From a Vehicle Gasoline Tank During
Refueling,” SAE Paper 860086.
[9] Gabele, P.A., and Knapp, K.T., (1993) “A
Characterization of Emissions from an Early Model
Flexible-Fuel Vehicle,” Journal of the Air & Waste
Management Association, 43, 736-744.
[10] Haskew, H.M., Cadman, W.R., and Liberty, T.F., (1990)
“The Development of a Real-Time Evaporative Emission
Test,” SAE Paper 901110.
[11] Hochhauser, A.M., and Campion, R.J., (1976) “An
Experimental Study of Vehicle Refueling Emissions,”
SAE Paper 760307.
[12] Cingle, P., and McClement, D., (1988) “A Study of
Uncontrolled Automotive Refueling Emissions,” CRC-
APRAC Project VE-6 Report, Prepared for the
Coordinating Research Council, Inc., by Automotive
Testing Laboratories, East LibertyOH.

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Investigation on evaporative emission from a gasoline polycarbonate fuel tank

  • 1. IJRET: International Journal of Research in Engineering and Technology eISSN: 2319-1163 | pISSN: 2321-7308 __________________________________________________________________________________________ Volume: 02 Issue: 12 | Dec-2013, Available @ http://www.ijret.org 46 INVESTIGATION ON EVAPORATIVE EMISSION FROM A GASOLINE POLYCARBONATE FUEL TANK S. Ajit1 , Thirumalini.S2 1 Master of Technology Automotive, 2 Professor, Department of Mechanical Engineering, Amrita School of Engineering ajitnair90@gmail.com Abstract It is estimated that about 15 to 20 percent of the vehicle hydrocarbon (HC) emission were due to evaporation of fuel. Hence a need was felt to understand the extent of evaporative emission from gasoline fuel system. A polycarbonate fuel tank that is predominantly used in two wheeled vehicles is considered for study. Emission can surface to atmosphere in three modes; diffusion through fuel tank wall, escaping through vent in tank and when fuel tank cap is opened for refueling. The average temperature condition which prevails in south India which is in the range of 27o C to 34o C was considered. From which temperatures which were at proximity to peak high and low day time were chosen. The complete set up was placed in open atmosphere to replicate the working environment. The emission constituents and its levels were measured by conducting the test particularly for averaged out day time high and low temperature condition. Further diffusion test was conducted within a range of 34o C to 36o C, this temperature is considered to be range of maximum temperature which prevails in south India. From which a temperature was chosen and the test was conducted. This comparative study gives an indication of emission and its quantity from the fuel tank at the ambient temperature. Keywords: Evaporative Emission, Fuel Tank, HC Emission ----------------------------------------------------------------------***----------------------------------------------------------------------- 1. INTRODUCTION Emission from the tail pipe is always considered the major cause of concern, where by evaporative emissions are ignored. Diurnal emissions are a type of evaporative emission that originate from the vehicle fuel tank as the fuel vaporizes due to the daily ambient temperature variations [1] . Two wheeled vehicles occupy a larger space on Indian roads [2] .Diurnal emissions are prevalent in the polycarbonate fuel tank which is commonly used in two wheeled vehicles. These were not sensitive to fuel tank capacity or vehicle refuelling system geometry or configuration [3] .Hence it is a surface phenomenon. This emission has become a cause for concern as fuel can evaporate from the tank which goes in to the atmosphere and reacts with air to form harmful pollutants. Under Indian condition where the vehicle is commonly parked in an open space are more prone to this type of Diurnal emission. Emission rate increases with both surrounding temperature and fuel volatility [4] . Evaporation led to permeation of fuel through fuel tank walls and escaped through vent which reached the outer environment. Fuel can also escape to atmosphere, when the fuel tank cap is open for refuelling. When the dispensed fuel temperature was higher than the fuel tank temperature, vapour growth occurred [3] . Permeation can be checked by heating up the fuel from 15.6o C to 28.9o C (60–84 F) within a period of 1 h as prescribed by the United States Environmental Protection Agency (US Environmental Protection Agency, 1991, 1992, 1994) and CONCAVE (CONCAWE, 1987, 1988, 1990)[1] . The tests were performed using a mini-SHED, which is a structure designed to enclose a fuel-tank instead of the entire vehicle [5] . Experiments were performed such that the quantities of emission constituents were measured and a comparative study was done for various temperatures. 2. EXPERIMENTATION PROCEDURE During this experiment, a poly carbonate fuel tank of capacity 5000cc was used. The maximum exposed surface area to air, in tank, occurred at capacity of 1000cc of gasoline. Hence 1000cc of fuel was considered for study. 2.1 Permeability Test of Fuel Tank The fuel tank was placed in a mini SHED, at ambient condition. As shown in Fig: 1 emission gas analyzer probe was introduced in the sealed chamber in order to measure the constituents of emission and its quantity. This tank had a capacity to retain heat, there by accelerated the experimental condition. Initially the ambient temperature and temperature inside the air-tight tank is measured. The whole set up is kept in an open environment and the constituents are measured in time steps of 10 minutes. This emission variation along with time is plotted and that gives a clear picture of time varying scale of emission constituents.
  • 2. IJRET: International Journal of Research in Engineering and Technology eISSN: 2319-1163 | pISSN: 2321-7308 __________________________________________________________________________________________ Volume: 02 Issue: 12 | Dec-2013, Available @ http://www.ijret.org 47 Fig: 1 Permeability Test on Fuel Tank 2.2 Break out Fuel Test The ambient temperature is noted, as it must be correlated with the averaged maximum or minimum day time temperature which prevails in south India (11.0183° N, 76.9725° E). In this test, the fuel tank was placed in the open environment for 30 minutes as shown in Fig: 2, in order to reach a thermodynamic equilibrium. Hence this in turn will increase the temperature of fuel inside. After 30 minutes of time the fuel tank cap is open and thus the fuel escaped was measured with emission gas analyzer. The analyzer indicates the value of the emission constituents which escaped while opening cap of the fuel tank.The probe was kept at a distance of 1 cm from the opening of the fuel tank. The dilute fuel vapour will be sensed by the probe which indicates the actual condition of the fuel in atmosphere. Fig: 2 Break Out Fuel Test 3. RESULT AND DISCUSSION 3.1 Break-Out Fuel Test at 29.8o c The maximum surface area was considered, for the ideal case. The fuel had a surface area of 263.4 cm2 which is in contact with air. HC vapour's presence was more when in compare with NO, which is indicated as in Fig 3 and 4. During the initial 30 minutes of tank's exposure to environment. The ambient temperature increased the kinetic energy of the top layer of liquid fuel particles such that it escaped the liquid boundary and attained gaseous state. After which the temperature of the liquid fuel reduced as the heat was carried away by the gaseous particles. This heated the surrounding air of gaseous particles thereby made nitrogen and oxygen which were the components of air present in tank, to react with each other. Thus this produced NO. When the tank cap was opened after 30 minutes, the vapour pressure of the fuel tried to equalize with atmospheric pressure. Hence vapour in the form of HC and NO shot up. This dipped as it matched with atmospheric pressure. Fig: 3 NO Vs Time at 29.8 o C Fig: 4 HC Vs Time at 29.8 o C 3.2 Break-Out Fuel Test at 34o c The kinetic energy of top level of fluid increased with the increase in ambient temperature and hence the occurrence of NO and HC vapours were high at 34o C. This vapour accumulated inside the tank in the initial 30 minutes of experiment, when the fuel tank was kept in open space. After 30 minutes the fuel tank cap is opened to allow the fuel vapour to escape out of the tank, during which the measurement of the emission is made, which gave a plot as in the Fig 5 and 6.From 0 10 20 30 40 0 10 20 30 40NOinPPM Time in Minutes 0 1000 2000 3000 4000 5000 0 10 20 30 40 HCinPPM Time in Minutes
  • 3. IJRET: International Journal of Research in Engineering and Technology eISSN: 2319-1163 | pISSN: 2321-7308 __________________________________________________________________________________________ Volume: 02 Issue: 12 | Dec-2013, Available @ http://www.ijret.org 48 both the breakout fuel test with different ambient temperatures showed noticeable increase in the emissions level. Fig 5 HC Vs Time at 34 o C Fig 6 d NO Vs Time at 34 o C 3.3 Emission Due to Diffusion The diffusion of the fuel through the fuel tank membrane was checked at 32o C by using a mini SHED. During this experiment it was evident that the HC vapour emitted through the vent and percolated through the fuel tank walls. The HC content gradually went up to a point and then decreases as shown in Fig 7 .But the presence of NO which is visible from Fig 8 was very low, such that it is neglected. This is because the fuel in fuel tank is cooled by evaporative cooling and it starts cooling the surrounding. As it is place in SHED, confined domain, evaporative cooling effect reduced mechanism of NO formation. Fig 7 HC Vs Time at 32o C This experiment was conducted for about 50 minutes, as per the EPA norms. The emission thus got was only for a stipulated time. It may vary according to the quantity of exposure to heat and time for which the tank is exposed. Fig 8 NO Vs Time at 32o C CONCLUSIONS From the result obtained, it was evident that the occurrence of evaporative emission increased with the increase in the ambient temperature condition. This experiment gives a clear picture of impact of environmental temperature effects by ignoring the temperature occurring (ex:engine) from the vehicle. The constituent like HC was predominant in the beginning and it gradually decreased at the end. Certain other constituents like CO CO2 and NO were found only at higher temperatures. It also stressed the need for eliminating the emission from the fuel tank through vent in the tank and due to diffusion through the fuel tank walls. However this emission might vary based on the climatic topography of the region. 0 500 1000 1500 2000 2500 3000 3500 4000 0 10 20 30 40 HCinPPM Time(Min) 0 20 40 60 80 100 120 0 10 20 30 40 NOinPPM Time (Min) 0 200 400 600 800 1000 1200 1400 1600 1800 2000 0 20 40 60 HCinPPM TIME(min) -1 0 1 2 3 4 5 6 0 20 40 60 NOinPPM Time (min)
  • 4. IJRET: International Journal of Research in Engineering and Technology eISSN: 2319-1163 | pISSN: 2321-7308 __________________________________________________________________________________________ Volume: 02 Issue: 12 | Dec-2013, Available @ http://www.ijret.org 49 REFERENCES [1] H. Van der Westhuisen et al 2004 “Evaluation of evaporative emissions from gasoline powered motor vehicles under South African conditions”, Elsevier Atmospheric environment Vol 38 pp 2 [2] Indian Road Transport Year Book 2010- 2011 [3] Braddock, J. N., Gabele, P. A., and Lemmons, T. J.,(1986) “Factors Influencing the Composition and Quantity of Passenger Car Refueling Emissions – Part 1,” SAE Paper 861558. [4] Smith, M., (1972) “An Investigation of Passenger Car Refueling Losses,” SAE Paper 720931 [5] Giorgos Mellios et al 2009, “A vehicle testing programme for calibration and validation of an evaporative emissions model” Elsevier fuel pp 2 [6] United States Environmental Protection Agency, (2001) “Evaluating Resting Loss and Diurnal Evaporative Emissions Using RTD Tests,” Assessment and Modeling Division,EPA420-R-01-018, M6.EVP.001, Ann Arbor, MI. [7] Reuter, R.M., Benson, J.D., Brooks, D.J., Dunker, A.M., Gorse, R.A. Jr, and Koehl, W.J., (1994) “Sources of Vehicle Emissions in Three Day Diurnal SHED Tests – Auto/Oil Air Quality Improvement Research Program,” SAE Paper 941965. [8] Furey, R., and Nagel, B., (1986) “Composition of Vapor Emitted From a Vehicle Gasoline Tank During Refueling,” SAE Paper 860086. [9] Gabele, P.A., and Knapp, K.T., (1993) “A Characterization of Emissions from an Early Model Flexible-Fuel Vehicle,” Journal of the Air & Waste Management Association, 43, 736-744. [10] Haskew, H.M., Cadman, W.R., and Liberty, T.F., (1990) “The Development of a Real-Time Evaporative Emission Test,” SAE Paper 901110. [11] Hochhauser, A.M., and Campion, R.J., (1976) “An Experimental Study of Vehicle Refueling Emissions,” SAE Paper 760307. [12] Cingle, P., and McClement, D., (1988) “A Study of Uncontrolled Automotive Refueling Emissions,” CRC- APRAC Project VE-6 Report, Prepared for the Coordinating Research Council, Inc., by Automotive Testing Laboratories, East LibertyOH.