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ACEE – Volume 02(2), 80-94
Advances in Civil and Environmental Engineering
www.jacee.us - copyright © 2013-2014 Jacee.us official website.
ENERGY, EXERGY, ENVIRONMENT AND RISK (EEER)
ANALYSES OF R600A AS A REPLACEMENT OF HFC
REFRIGERANT FOR HOUSEHOLD REFRIGERATOR SYSTEM
Alireza Noorpoor 1*, Mohanna Akhlaghi 1 , Sultan hosein Fattahi 2
1 Graduate Faculty of Environment, University of Tehran (UT), Tehran, Iran
2 Emersun Industrial Groups, Tehran, Iran
* Corresponding author, E-mail: [email protected]
Abstract
Energy-Exergy analysis was applied to investigate environmental impact of R134a in general, and
the effect of change of variables on TEWI in particular. We study on isobutene (R600a) as an
environment-friendly refrigerant with zero ozone depletion potential (ODP) and negligible global
warming potential (GWP), to replace R134a in domestic vapor-compression refrigeration system. Then
FMEA method for risk analysis carried out based on experimental result and presented for predicting
the flammability of pure hydrocarbon of household refrigerator. The result shows average coefficient of
performance (COP) using R600a is higher than from R134a. The system consumed less energy by
using R600a, which shows that it can be used as replacement for R134a in domestic refrigerator.
Furthermore, when the refrigerator is working with R600a type compressor, have a total TEWI about
42% less than HFC refrigerators. This article discusses the relations between environmental impact and
thermodynamics in general, and the thermodynamic property exergy in particular.
Keywords: Exergy analysis, Energy, Domestic refrigerator, Risk analysis, R600a, R134a, TEWI
Nomenclature
Exergy rate (kW)
RC refrigerant charge (kg)
GWP Global warming potential
T Temperature (K)
Work rate (kW)
ISSN 2345-2722
Alireza Noorpoor et al. Journal of Advances in Civil and Environmental Engineering, Volume 02(2), 80-94
18
TEWI Total Equivalent Warming (kg CO2)
ODP Ozone Depletion Potential
accidental refrigerant leaks per year
(% refrigerant charge/year)
refrigerant power (kW)
COP coefficient of performance
Exergetic efficiency
CO2 emission from power conversion ( /kWhe)
1. Introduction
In recent years, the term global warming potential is become a serious environmental problem,
which is hard to be solved without focus on energy consumption (Kayukawa, 2002). All products
include vapor compression systems embodied green-house gas, hence effective solution for climate
change require fundamental transformation of the energy is used (ZhongXiang, 2009). Most modern
refrigeration are based on vapor compression system (Montreal Protocol, 1987). Vapor compression
refrigeration systems have both a direct and an indirect contribution to global warming (Aprea et al.,
2012).
First generation of the refrigerants mostly used ammonia, carbon dioxide, sulphur dioxide and
methyl chloride as a refrigerant which were found to be toxic or hazardous (Bolaji, 2010). However, in
1931 alternative refrigerants were introduced by a shift to chlorofluorocarbons (CFCs) and hydro-
chlorofluorocarbons (HCFCs) for safety issues (Bolaji, 2005). CFCs and HCFCs have many suitable
properties, for example, stability, non-toxicity, non-flammable, good material compatibility and good
thermodynamic properties, make theme a popular refrigerant in large, industrial systems especially for
air-conditioning and refrigerating systems (Radermacher et al., 1996).
Release of CFCs and HCFCs to atmosphere which are large class of ozone-depleting substances,
migrate to the stratosphere. Later, chlorine atoms began to react with ozone and convert theme to
oxygen (Bolaji, 2010). Depletion of the earth’s ozone layer that protect the earth’s surface from UV
radiation, led to phase out of halogenated fluids. Developed countries phased out the CFCs since 1996,
and in 2010, producing and using of CFC refrigerant will be prohibited in all over the world (UNEP,
2003; Sattar et al., 2007). In recent years the European Parliament set a regulation of F-Gases phase out
(Bansal et al., 2011).that prohibits the using of refrigerants having GWPs more than 150. Such
regulation will do so by 2011 (Regulation (EC) n.842/2006 of the European Parliament and of the
Alireza Noorpoor et al. Journal of Advances in Civil and Environmental Engineering, Volume 02(2), 80-94
18
Council, 2006). So it`s obvious that synthetic refrigerants are no more sustainable from an
environmental perspective due to their ozone depleting potential (ODP) and global warming potential,
therefore Refrigerants such as HFCs have to be replace by alternatives with low global warming
potential (Colbourne et al., 2013). HFCs have high volatility and very low solubility in water and when
releases into the environment, these compounds reside in the atmosphere for years (Wen-Tien, T.,
2005).
Additionally, some problems such as high pressure drop in compressor and evaporator occurs by
using R134a (Smith et al., Energy 2001). The global warming potential for R134a is high so it will be
replaced with a low GWP fluid (Zilio et al., 2011; Bolaji, Energy 2010).
The new generation of refrigerant must offer both high efficiency and low global warming potential
(GWP). Furthermore the atmospheric lifetime should be noted (Calm, Refrigeration 2008). Mohanraj
reported that natural refrigerants (hydrocarbon refrigerants) are the best choice as substitutes for
halogenated refrigerants in domestic refrigerators (Mohanraj et al., 2006). Using hydrocarbon mixture
as a refrigerant, leads to the changes in refrigerator temperature occur faster and the ON time ratio of
the compressor is less than that of using R134a thus reduction in the compressor’s energy consumption
(Mohanraj et al., 2009; Mani et al., 2008). Refrigeration proportion of the worldwide energy
consumption is about 15% (Landymore, 2007; Annual energy review 2010). The latent heat of
hydrocarbons is significantly better than R134a, i.e. the amount of heat absorbed during evaporation is
much higher per kg of refrigerant circulating in the system, and therefore the amount of refrigerant
charge can be reduced (Rasti et al., 2012). Maclaine-cross (1997) measures on various systems and
reported that the use of hydrocarbon refrigerants sometimes reduction the energy consumption about
20% in comparison with R12 and R134a (Maclaine-cross, 1997). In addition R600a has the half price
of R134a which shows the R600a is economically beneficial (Joybari et al., 2013). The results showed
that the R290 could not be used as a refrigerant replacement due to its high operating pressure
compared to R134a (Sattar et al., 2007). Although R600 and R600a offer many desirable characteristics
such as in operating pressure, mass flow rate, discharge temperature and high coefficient of
performance (COP), the compressor should be changed due to its mismatch in volumetric cooling
capacity (VCC) (Mohanraj et al., 2008). Safety guidelines for different refrigerants can be found
elsewhere such as the handbook of GTZ Proklima (Colbourne et al., 2010). R600a is not using in North
America because of the flammability risk and explosion hazards in domestic refrigerators (Calm.,
2008), while in European countries R600a is the most popular refrigerant to use in domestic
Alireza Noorpoor et al. Journal of Advances in Civil and Environmental Engineering, Volume 02(2), 80-94
18
refrigerators (Bansal et al., 2011).Additionally, among the hydrocarbon refrigerants, R600a is used
more than 95% of market share in many countries (RTOC., 2006).
To optimize refrigeration cycles offer potential energy and cost savings. The refrigeration cycle can
best be evaluated by energy and exergy analyses (Mokhatab et al., 2014).
2. Material and methods
The test ring tabulated to the experiment is a vapor compression refrigeration system developed in
the form a single temperature domestic refrigerator which manufactured to work with 145g of R134a
refrigerant. The schematic diagram and general specifications are summarized in Figs. 1, respectively.
The experimental refrigerator has a capacity of 410L, the main loop of the system under study consist
of four basic components, i.e., a compressor, an evaporator, a condenser, and capillary tubes, as shown
in Figure. 1.
2.1.Testing procedure
Experiments were conducted in a test room with environmental temperature of 25°c.The
refrigerator was instrumented with two pressure gauges and thermocouples at the inlet and outlet of the
compressor, evaporator, capillary tube and condenser for measuring the suction and discharge pressure
and temperature.
Figure 2 shows the present experimental path of the measurements for R134a on a pressure-
enthalpy diagram and a temperature-entropy diagram (T-S diagram), respectively.
Figure. 1 Schematic of the vapor-compression household refrigeration system.
Alireza Noorpoor et al. Journal of Advances in Civil and Environmental Engineering, Volume 02(2), 80-94
18
Table. 1 Properties of the case study refrigeration system
Property Value Unit
Total volume 410 lit Net volume of freezer 98 lit Net volume of fresh food box 264 lit Ice making capacity 4.5 lit/24h
Climate Temperate
Total net volume 352 lit Voltage 220-240 vol Refrigerant 150 gr Defrost R134a
Capillary tube length (No frost system) 3.55 m
Table. 2 Thermodynamic conditions in different points of the refrigeration cycle
points h P s T v x
1 236.4 114.9 0.9487 -23.3 0.1689
2 290.8 820.5 0.991 54.4 0.02833
3 131 820.5 0.4702 32.2 0.005671
4 131 114.9 0.5269 -23.3 0.0865 0.351
Figure. 2 Pressure-enthalpy diagram of R134a Figure. 3 Temperature-entropy diagram
2.3. Energy, Exergy and Environmental Analyses
In this section we employ energy-exergy analysis for tow gases (R134a and R600a) to minimization
GWP of refrigerator systems.
In real compressor:
(1)
In condenser:
Exergy balance in condenser equation:
-50 0 50 100 150 200 250 300 350 4000x10
02x10
24x10
26x10
28x10
210
310
310
310
310
32x10
32x10
32x10
32x10
32x10
33x10
3
h [kJ/kg]
P [
kP
a]
-23.3°C
32.2°C
54.4°C
0.2 0.4 0.6 0.8
0.3
582
0.3
901
0.9
487
0.9
91 k
J/kg
-K
-0.25 0.00 0.25 0.50 0.75 1.00 1.25
-40
-20
0
20
40
60
80
100
120
140
s [kJ/kg-K]
T [
°C
]
114.9 kPa
820.5 kPa
0.2 0.4 0.6 0.8
0.0
0084
0.0
28
0.0
59
0.1
7 m
3/k
g
Alireza Noorpoor et al. Journal of Advances in Civil and Environmental Engineering, Volume 02(2), 80-94
18
(2)
Exergy destruction:
[ ( )] ( ) (3)
Exergy efficiency:
(
( )
[ ( )]) (4)
In capillary tube:
(5)
[ ( )]
(6)
In evaporator:
(7)
[ ( )] [ ( )] (8)
(
( )
[ ( )]) (9)
Now we can calculate the exergy destruction of the entire cycle:
(10)
exergy efficiency of the entire cycle:
(11)
The coefficient of performance of the Carnot cycle refrigerator:
(12)
Alireza Noorpoor et al. Journal of Advances in Civil and Environmental Engineering, Volume 02(2), 80-94
18
The calculated TEWI is sensitive to assumptions of the system lifetime, emission losses, and the
integration time horizon chosen to calculate global warming potential (GWP) values as well as the
source and consumption of energy.
The TEWI is calculated as (Aprea et al., 2012):
TEWI=CO + CO [kg Co2] (13)
CO =RC [ + (
)].V.GWP [kg CO2] (14)
CO =
.H.V [kg CO2] (15)
Table. 3 Parameters of TEWI
Parameter value
H 8760 h 10% year
100%
V 7 years
575 kg co2/kwh
Table. 4 Properties of some common refrigerants.
Global Warming Potential for Given Time Horizon
Industrial Designation
or Common Name Chemical Formula
Lifetime
(years) 20
100
500
HFC-134a 14 38300
1430
435
Isobutene-R600a ( ) 12 <20
<20
<3
3. Result and Discussion
3.1. Inlet temperature of compressor
When T1 is raised, while evaporator pressure is fixed, coefficient of performance and cooling
capacity are increased. Conversely the compressor work and total exergy destruction decreased (see
table 5). Table 4 based on the equations in section 1.
Table. 5 effects of inlet temperature of compressor on different variables using R134a
T1 W
com
Q
evap
Eff
comp COP
Des
com
Des
Evap
Ex
Evap
Ex
Comp
Des
total
Rand
Total
-29 276.9 -117 0.0018 0.42 278.0 -265.6 -8.87 276.9 285.7 3.21
-23 54.18 105.6 0.7558 1.95 12.3 239.7 8.01 54.18 46.17 14.78
-17 49.36 110.5 0.8545 2.24 6.6 250.5 8.38 49.36 40.99 16.97
-11 44.52 115.3 0.9744 2.59 1.0 261.3 8.74 44.52 35.78 19.64
-5 39.65 120.2 1.1240 3.03 -4.4 272 9.11 39.65 30.54 22.98
Alireza Noorpoor et al. Journal of Advances in Civil and Environmental Engineering, Volume 02(2), 80-94
18
Table. 6 effects of inlet temperature of compressor on different variables using R600a
T1 W
com
Q
evap
Eff
comp COP
Des
com
Des
evap
Ex
Evap
Ex
Comp
Des
total
Rand
Total
-29 504.6 -141.8 0.001188 0.281 506 -322 -10.75 504.6 515.4 2.131
-23 115.6 247.2 0.6176 2.138 41.73 560.8 18.74 115.6 96.9 16.21
-17 106.6 256.2 0.6877 2.402 31.14 581.1 19.42 106.6 87.22 18.21
-11 97.52 265.3 0.7715 2.721 20.65 601.4 20.11 97.52 77.41 20.62
-5 88.26 274.6 0.8736 3.111 10.24 621.8 20.82 88.26 67.45 23.58
Increasing energy efficiency can reduce environmental impact by reducing energy losses. Within
the scope of exergy methods, as discussed, such activities lead to increased exergy efficiency and
reduced exergy losses. Increased efficiency reduces the requirement for new facilities for the
production, transportation, transformation and distribution of the various energy forms, and the
associated environmental impact of these additional facilities. To control pollution, efficiency
improvement actions often need to fuel substitution. Environmental protection project which
undertaken at the regional or national levels, are more effective than individual projects (Dincer et al.,
2007).
Figure. 4 Variability exergy efficiency versus inlet
temperature of compressor (see table 2).
Figure. 5 TEWI of R134a and R600a versus inlet
temperature of the compressor
3.2. Inlet pressure of compressor
As shown in table 7, with reducing the inlet pressure of compressor, the exergy efficiency increase
at a constant temperature. However, it should be noted that there are some limitations on reducing
pressure.
y = 0.4545x + 24.956 R² = 0.9911
y = 0.4087x + 25.376 R² = 0.9924
0.00
5.00
10.00
15.00
20.00
25.00
-25 -20 -15 -10 -5 0
Ex-R
and
(%)
T1(k)
R134a
R600a
Linear (R134a)
Linear (R600a)
0
2000
4000
6000
8000
10000
12000
14000
16000
18000
-40 -30 -20 -10 0
TEW
I
T1
R600a
R134a
Alireza Noorpoor et al. Journal of Advances in Civil and Environmental Engineering, Volume 02(2), 80-94
11
Table. 7 effects of inlet pressure of compressor on different variables
P1 P4 T4 s1 s4 v1 v4 h1 h4 Wcomp Qevap Effcomp COP
39.9 39.9 -44.66 1.04 0.57 0.50 0.27 238.90 131 51.94 107.9 1.33 2.08
64.9 64.9 -35.39 1.00 0.55 0.31 0.16 238.10 131 52.73 107.1 1.06 2.03
89.9 89.9 -28.67 0.97 0.54 0.22 0.11 237.20 131 53.56 106.3 0.88 1.98
114.9 114.9 -23.3 0.95 0.53 0.17 0.09 236.40 131 54.43 105.4 0.75 1.94
Table. 8 Effect of inlet pressure of compressor on exergy variations in refrigeration cycle
P1 Des
com
Des
con
Des
eva
Des
capi
Rand
comp
Rand
evap
Ex
Evap
Ex
Comp
Des
total
Rand
Total
114.9 12.6 315 239.1 16.9 0.7686 0 0.3935 0 46.44 14.68
89.9 5.849 315 243.8 19.88 0.8908 0 0.3472 0 45.51 15.04
64.9 -2.81 315 249.2 24.07 1.053 0 0.3025 0 44.62 15.4
39.9 -15.33 315 255.9 30.75 1.295 0 0.2565 0 43.76 15.75
Figure. 6 TEWI versus inlet pressure of the
compressor
Figure. 7 TEWI versus total exergy destruction in different
inlet pressure of compressor
3.3. Outlet temperature of condenser
As can be seen in Table 5, the reduction of temperature at point No.2 has led to increase in exergy
efficiency and the coefficient of performance. It stems from the less work required from the
compressor. Nevertheless, the limitations of the design and selection of the compressor and condenser,
prevent the temperature reaching below the desire level.
Table. 9 effects of outlet temperature of condensor on different variables
T2 Wcomp Qcond Effcomp COP Des
com
Des
con
Rand
com
Ex
Com
Ex
Evap
Des
total
Rand
Total
40 39.63 145 1.03 2.66 -1.17 286.5 1.03 39.63 7.99 31.64 20.16 42.4 42.18 147.6 0.97 2.50 1.24 291.4 0.97 42.18 7.99 34.19 18.95 44.9 44.7 150.1 0.91 2.36 3.62 296.3 0.92 44.7 7.99 36.71 17.87 47.3 47.22 152.6 0.87 2.23 5.97 301.2 0.87 47.22 7.99 39.23 16.92 49.8 49.72 155.1 0.82 2.12 8.28 306 0.83 49.72 7.99 41.73 16.07 52.2 52.21 157.6 0.78 2.02 10.58 310.8 0.80 52.21 7.99 44.22 15.3 54.7 54.7 160.1 0.75 1.93 12.85 315.5 0.77 54.7 7.99 46.71 14.61 57.1 57.18 162.6 0.71 1.84 15.09 320.3 0.74 57.18 7.99 49.19 13.97 59.6 59.66 165.1 0.69 1.77 17.32 325 0.71 59.66 7.99 51.67 13.39 62 62.13 167.5 0.66 1.70 19.53 329.7 0.69 62.13 7.99 54.14 12.86
3400
3450
3500
3550
3600
3650
3700
3750
0 50 100 150
TEW
I
P1
114.9
89.9
64.9
39.9,
3400
3450
3500
3550
3600
3650
3700
3750
43 44 45 46 47
TEW
I
DES-total
Alireza Noorpoor et al. Journal of Advances in Civil and Environmental Engineering, Volume 02(2), 80-94
18
Figure. 8 Exergy efficiency versus outlet
temperature of the condenser
Figure. 9 TEWI versus total exergy efficiency in
different outlet temperature of condenser
3.4. Effect of changing pressure in condenser
Changes in the outlet pressure of the compressor will lead to variations in refrigerant pressure in the
condenser. Care must be taken in compressor limitation when pressure increases, therefore the
refrigerant could not be achieved to saturated state. In general, by given the initial assumptions, rise in
the pressure, at a constant temperature, for condensing procedure in the condenser, is one of the
effective ways to raise the efficiency of the cycle.
Table. 10 effects of outlet temperature of condenser on different variables
T4 P2 Wcomp Qcond Qevap COP Rand
com
Rand
eva
Ex
Com
Ex
Evap
Des
total
Rand
Total
15.7 800 54.79 22.9 -31.89 0.582 0.7542 0.7041 54.79 -2.418 57.21 4.412
-23.3 900 52.99 192.6 139.6 2.635 0.8236 0.3935 52.99 10.58 42.4 19.97
-23.3 1000 51.09 190.7 139.6 2.732 0.8932 0.3935 51.09 10.58 40.51 20.71
-23.3 1100 49.1 188.7 139.6 2.843 0.9649 0.3935 49.1 10.58 38.51 21.56
-23.3 1200 46.98 186.6 139.6 2.972 1.041 0.3935 46.98 10.58 36.4 22.53
-23.3 1300 44.72 184.3 139.6 3.122 1.123 0.3935 44.72 10.58 34.14 23.67
-23.3 1400 42.29 181.9 139.6 3.302 1.215 0.3935 42.29 10.58 31.7 25.03
-23.3 1500 -106 33.62 139.6 1.317 -0.367 0.3935 -106 10.59 -116.6 9.986
3.5. Exergy-Environment
Using exergy as a tool can reduce energy consumption and environmental degradation. The second
law of thermodynamics is discussed to providing insights into environmental impact. Following this,
exergy found to be an effective measure of the potential of a substance to impact the environment.
0
5
10
15
20
25
0 10 20 30 40 50 60 70
Ran
d-t
ota
l
T2
0
1000
2000
3000
4000
5000
0 5 10 15 20 25
TEW
I
Rand-total
Alireza Noorpoor et al. Journal of Advances in Civil and Environmental Engineering, Volume 02(2), 80-94
89
Figure. 10 TEWI of R134a and R600a versus total exergy
efficiency of cycle Figure. 11 TWEI of assessed years
3.6. Risk analysis
However hydrocarbons pose fire and explosion hazards, so if used in domestic refrigeration
systems, the impact on safety should be negligible. Appropriate equipment and design could reduce the
risk of using R600a in domestic refrigerators. Data has been gathered from industries in Iran, then
FMEA method used to determination of value of risk.
According to results of table11 and table 12, which indicate two major potential failure modes in
household refrigerator show the risk of using R600a is in safe range.
4. Concolution
Using of hydrocarbons with a zero ODP, and a lower GWP in compare with R134a for household
refrigerator systems help to reduce energy consumption. Furthermore, when the refrigerator is working
with R600a type compressor, have a total TEWI about 42% less than HFC refrigerator. In this research,
the relation between exergy efficiency and its impact on environment have been investigated. The
results show that, by increasing in total exergy efficiency, total equivalent warming impact has been
reduced generally. R600a demonstrate better cop and exergy efficiency, which make R600a a suitable
substitution for R134a refrigerant in domestic refrigerator system.
Acknowledgments
We greatly acknowledge Emersun Industry Group for funding and supporting the project.
02000400060008000
1000012000140001600018000
0 10 20 30
TEW
I
Exergy efficiency
R600a
R134a
0
50000
100000
150000
200000
250000
300000
20 100 500
TEW
I
Years
R134a
R600a
Alireza Noorpoor et al. Journal of Advances in Civil and Environmental Engineering, Volume 02(2), 80-94
88
Table. 11 Identification and Risk Assessment Form1
Identification and evaluation of the risk Reformation activity Evaluation of the risk after
reformation
raw
Fu
nct
ion
haza
rd
con
seq
uen
ce
Ris
k
sou
rce
Cu
rren
t
Con
tro
l
Sev
erit
y
Prob
ab
ilit
y
Det
ect
ion
RP
N
Rec
om
me
nd
ed
act
ion
s
Act
ion
s
For
furt
her
Inves
tigati
on
Sev
erit
y
Prob
ab
ilit
y
Det
ect
ion
RP
N
1
Tra
nsp
ort
atio
n
Hit
the
refr
iger
ator
Dam
age
to t
he
cooli
ng s
yst
em R
efri
ger
ant
leak
age
–
Cre
ate
a fi
re
Lac
k o
f ap
pro
pri
ate
safe
guar
ds
on t
he
syst
em -
lac
k o
f pro
per
trai
nin
g
to t
he
tra
nsp
ort
work
ers
Pac
kin
g w
ith c
arto
n a
nd p
alle
t -
Gas
det
ecto
rs
3
3
4
36
Per
sonal
tra
inin
g t
o h
ow
tra
nsp
ort
the
refr
iger
ator-
pro
vid
e le
ak
det
ecti
on g
uid
elin
es-
supply
a f
ire
exti
nguis
her
in a
ref
riger
ator
box
Educa
tion m
ethods
for
corr
ect
tran
sport
atio
n o
f re
frig
erat
ors
-
Lea
k d
etec
tion
aft
er i
nst
alla
tion
3
2
3
18
Alireza Noorpoor et al. Journal of Advances in Civil and Environmental Engineering, Volume 02(2), 80-94
88
Table. 12 Identification and Risk Assessment Form2
Identification and evaluation of the risk Reformation
activity
Evaluation of the risk
after reformation
raw
Fu
nct
ion
haza
rd
con
seq
uen
ce
Ris
k
sou
rce
Cu
rren
t
Con
tro
l
Sev
erit
y
Prob
ab
ilit
y
Det
ect
ion
RP
N
Rec
om
men
ded
act
ion
s
Act
ion
s F
or
Fu
rth
er
Inves
tigati
on
Sev
erit
y
Prob
ab
ilit
y
Det
ect
ion
RP
N
2
wel
d
Def
ect
in r
efri
ger
ant
syst
em
Lea
kag
e- i
gnit
ion
Not
know
ing h
ow
to p
roper
ly w
eld -
the
lack
of
stan
dar
d t
ools
- l
ack o
f
pre
cisi
on i
n t
he
wel
din
g
Wel
din
g e
duca
tion
- le
akag
e te
st
3 4 4 48
Per
sonal
tra
inin
g t
o h
ow
wel
d-p
rovid
e le
ak d
etec
tion g
uid
elin
es-
supply
a fi
re e
xti
nguis
her
in a
ref
riger
ator
box
Educa
tion m
ethods
for
corr
ect
wel
din
g-
Lea
k d
etec
tion a
fter
inst
alla
tion
3 3 3
27
References
Kayukawa, Y., 2002. Study of Thermodynamic Properties for Novel Refrigerants with Rapid and Precise Density
Measurement Technique, The Center for Environment, Resources and Energy. 1-10.
ZhongXiang, Z., 2009. Multilateral trade measures in a post-2012 climate change regime? What can be taken from the
Montreal Protocol and the WTO? Energy Policy 37. 5105–5112
Montreal Protocol on substances that deplete the ozone layer., 1987. New York, NY,USA: United Nations (UN).
Alireza Noorpoor et al. Journal of Advances in Civil and Environmental Engineering, Volume 02(2), 80-94
88
Aprea, C. and Greco, A., 2012. An experimental evaluation of the greenhouse effect in the substitution of R134a with CO,
Maiorino Dipartimento di Ingegneria Industriale, Università di Salerno, via Ponte Don Melillo, 84084 Fisciano,
Salerno, ItalyDETEC, Università degli Studi di Napoli Federico II, P.le Tecchio 80, 80125 Napoli, Italy.
Bolaji, B.O., 2010. Experimental study of R152a and R32 to replace R134a in a domestic refrigerator.
Bolaji, B.O., 2005. CFC refrigerants and stratospheric ozone: past, present and future.In: Okoko E, Adekunle VAJ, editors.
Environmental Sustainability and Conservation in Nigeria. 231-239.
Radermacher, R. and Kim, K., 1996. Domestic refrigeration: recent development. International Journal of Refrigeration. 19,
61_69.
UNEP., 2003, Handbook for international treaties for protection of the ozone layers.6th ed. Nairobi, Kenya: United Nation
Environment Program.
Sattar, MA. Saidur, K., and Masjuki, HH., 2007. Performance investigation of domestic refrigerator using pure
hydrocarbons and blends of hydrocarbons as refrigerants. Proceedings of World Academy of Science, Engineering
and Technology. 23, 223-228.
Regulation (EC) n.842/2006 of the European Parliament and of the Council of 17 May 2006 on certain fluorinated
greenhouse gases. Off J Eur Union 2006. 49-161.
Colbourne, D. and Espersen, L., 2013. Quantitative risk assessment of R290 in ice cream cabinets, international journal of
refrigeration. 36, 1208-1219.
Wen-Tien, T., 2005. An overview of environmental hazards and exposure risk of hydrofluorocarbons (HFCs), Department
of Environmental Engineering and Science, Chemosphere. 61, 1539–1547.
Smith, S.J. Shao, L. and Riffat, S.B., Energy 2001. Pressure drop of HFC refrigerants inside evapourator and condenser
coils as determined by CFD. 70, 169-178.
Zilio, C. Brown, JS. Schiochet, G. and Cavallini, A., 2011. The refrigerant R1234yf in airconditioning systems. 36, 6110-
6120.
Bolaji BO., Energy 2010, Experimental study of R152a and R32 to replace R134a in a domestic refrigerator. 35, 3793-3798.
Calm, J.M., Refrigeration 2008. The next generation of refrigerants e historical review, considerations, and outlook. Int. J.
1123-1133.
Mohanraj, M., Muraleedharan, C., and Jayaraj, S., 2006. Natural refrigerants as the substitute for CFC/HFC refrigerants in
vapour compression refrigeration units: A review. Third Asian conference on refrigeration and air
conditioning,Seoul National University, Seoul, Korea. 373–376.
Mohanraj, M. Jayaraj, S. Muraleedharan, C. and Chandrasekar, P., 2009. Experimental investigation of R290/R600a
mixture as an alternative to R134a in a domestic refrigerator, International Journal of Thermal Sciences. 48, 1036–
1042.
Mani, K. and Selladurai, V., 2008. Experimental analysis of a new refrigerant mixture as drop-in replacement for CFC12
and HFC134a, International Journal of Thermal Sciences. 47, 1490–1495.
Landymore, K., 2007. Report Smartcool System Inc. Electrical energy reduction in refrigeration and air conditioning.
Annual energy review 2010. Report DOE/EIA-0384. USA: US Department of Energy; 2010. October 2011.
Rasti, M. Hatamipour, M. Aghamiri, S. and Tavakoli, M., 2012. Enhancement of domestic refrigerator’s energy efficiency
index using a hydrocarbon mixture refrigerant. 1807–1813.
Maclaine-cross, I. L., 1997. Why hydrocarbons save energy.AIRAH Journal. 51, 33–37.
Alireza Noorpoor et al. Journal of Advances in Civil and Environmental Engineering, Volume 02(2), 80-94
88
Joybari, M. Hatamipour, M. Rahimi, A. and Moharres, F., 2013. Exergy analysis and optimization of R600a as a
replacement of R134a in a domestic refrigerator system. 1-10.
Sattar, M. Saidur, R. and Masjuki, H., 2007. Pure butane as refrigerant in domestic refrigerator–freezer, in: GMSARN
International Conference on Sustainable Development: Challenges and Opportunities for GMS, Thailand. 12–14.
Mohanraj, M. Jayaraj, S. and Muraleedharan, C., 2008. Comparative assessment of environment-friendly alternatives to
R134a in domestic refrigerators Energy Efficiency. 1, 189–198.
Colbourne, D. Huhren, R. Schremph, B. Ederberg, L. and Hasse, V., 2010. Guidelines for the Safe Use of Hydrocarbon
Refrigerants. GTZ Proklima, Eschborn, Germany (Available from), (http://www.gtz.de/en/themen/umwelt-
infrastruktur/28719.ht).
Bansal, P., Vineyard, E., Abdelaziz, O., 2011. Advances in household appliances- A review. Appl. Therm. Eng. 31, 3748-
3760.
RTOC., 2006. UNEP Report of the Refrigeration, Air Conditioning and Heat Pumps Technical Options Committee.
Mokhatab, S. Mak, J. Valappil, J. and David Wood, A., 2014, Handbook of Liquefied Natural Gas, Chapter 4 – Energy and
Exergy Analyses of Natural Gas Liquefaction Cycles.
Dincer, I. and Rosen, M., 2007. Exergy:Energy, Environment and Sustainable Development. 1-451.