Accepted Manuscript Productivity enhancement of solar still by using porous absorber with bubble-wrap insulation
T. Arunkumar, A.E. Kabeel, Kaiwalya Raj, David Denkenberger, Ravishankar Sathyamurthy, P. Ragupathy, R. Velraj PII:
S0959-6526(18)31545-2
DOI:
10.1016/j.jclepro.2018.05.199
Reference:
JCLP 13056
To appear in:
Journal of Cleaner Production
Received Date:
14 January 2018
Accepted Date:
23 May 2018
Please cite this article as: T. Arunkumar, A.E. Kabeel, Kaiwalya Raj, David Denkenberger, Ravishankar Sathyamurthy, P. Ragupathy, R. Velraj, Productivity enhancement of solar still by using porous absorber with bubble-wrap insulation, Journal of Cleaner Production (2018), doi: 10.1016/j.jclepro.2018.05.199
This is a PDF file of an unedited manuscript that has been accepted for publication. As a service to our customers we are providing this early version of the manuscript. The manuscript will undergo copyediting, typesetting, and review of the resulting proof before it is published in its final form. Please note that during the production process errors may be discovered which could affect the content, and all legal disclaimers that apply to the journal pertain.
ACCEPTED MANUSCRIPT
Graphical Abstract
insulation front view, and (b) bottom view
ACCEPTED MANUSCRIPT
2
Productivity enhancement of solar still by using porous absorber with bubble-wrap insulation
3
T. Arunkumar*1, A.E. Kabeel*2, Kaiwalya Raj1, David Denkenberger3, Ravishankar
4
Sathyamurthy2,4,5, P. Ragupathy6, R. Velraj1
1
1Institute
5 6 7 8 9 10 11 12 13
for Energy Studies, CEG, Anna University, Chennai-600 025, Tamilnadu, India of Mechanical Power Engineering, Tanta University, Egypt 3Department of Civil and Architectural Engineering, Tennessee State University, Nashville, TN, USA 4Department of Mechanical Engineering, S.A. Engineering College, Chennai, Tamilndu, India 5Centre for excellence in energy and nano technology, S.A. Engineering College, Chennai, Tamilndu, India 6Aksheyaa College of Engineering, Pulidivakkam, Kancheepuram-603 314, Tamilnadu, India
14
Abstract
15
The present work involves a solar water de-salting system with carbon impregnated foam
16
(CIF) with bubble-wrap (BW) insulation for fresh water productivity enhancement. The said
17
solar water de-salting system is single slope solar still (SSSS) of area 0.50 m2. Four identical
18
SSSSs were constructed and the performance was evaluated in the same climatic conditions
19
of Chennai (13.08°N latitude, 80.27°E longitude). The CIF of diameter 0.17 m and thickness
20
of 0.015 m was allowed to float on the water surface. Since the CIF was open pore and
21
hydrophilic, the floating absorbers acted as thermal storage and increased the evaporative
22
surface area of the basin. The temperature distributions on the floating absorbers are
23
investigated with computational fluid dynamics (CFD) analysis. The result shows that the
24
simulation of temperature distribution has good agreement with experimentally recorded
25
data. Three modes of operation were tested: (i) SSSS without insulation, (ii) SSSS with BW
26
insulation and (iii) SSSS-CIF with BW insulation. The results were compared with a
27
conventional solar still (CSS) with sawdust insulation. The climatic parameters like wind,
28
ambient temperature, solar radiation and internal temperatures of the SSSS were measured at
29
frequent intervals of time. The water quality tests were carried out and their results were
2Department
1
Corresponding author:
[email protected] (AE. Kabeel),
[email protected] (T. Arunkumar)
[email protected] (Kaiwalya Raj),
[email protected] (David Denkenberger),
[email protected] (Ravishankar Sathyamurthy),
[email protected] (P. Ragupathy), and
[email protected] (R. Velraj). 1
ACCEPTED MANUSCRIPT 30
compared with rain water samples. The results showed that the productivity of the SSSS
31
without insulation, SSSS with BW insulation, SSSS-CIF with BW insulation and CSS with
32
sawdust insulation are 1.9 l/m2/day, 2.3 l/m2/day, 3.1 l/m2/day and 2.2 l/m2/day, respectively.
33
Keywords: single slope solar still; carbon impregnated foam; bubble wrap, desalination
34 35
1. Introduction
36
Prof. Stephen Hawking says that people must colonize another planet in next 100
37
years due to serious climate change, population growth and overdue asteroid strikes (Kharpal
38
and Arjun 2017). At the same time, ground water levels are decreasing at an accelerating rate
39
(Shiao et al. 2015). It is our responsibility to bring clean water to the next generation. A
40
sustainable way of producing fresh water is solar desalination with brackish water input with
41
minimal CO2 emissions. Solar stills are very well studied over last 30 years by scientists
42
worldwide. The basic idea is sunlight passing through a clear cover and being absorbed by a
43
black basin containing salty water. This heats the water, which evaporates and then
44
condenses on the cooler cover above. The pure water drains off and is collected. This
45
technology is old but effective for the present and future scenarios in remote places.
46
Renewable energy is a cleaner way of producing desalinated water in remote and arid regions
47
(Koroneos et al. 2007). Chafidz et al. (2016) designed and developed the portable and hybrid
48
solar-powered distillation system for generating freshwater in arid regions and coastal areas
49
in Saudi Arabia. The result concluded that the fresh water output from the sustainable solar-
50
powered distillation system was 11.53 L/h.
51
Manokar et al. (2018) experimentally studied a photovoltaic-thermal (PVT) solar still
52
varying two parameters: (i) with and without insulation, and (ii) with and without water flow
53
over the cover. The dimension of the solar still was 1810 mm × 920 mm × 150 mm. The
54
basin of the solar still consisted of a polycrystalline PV panel of efficiency of 13-16%. The
55
result concluded that the sustainable production of an inclined solar panel solar still with side
56
wall insulation was 7.3 kg/m2/day. Abujazar et al. (2018) tested a stepped solar still for sea
57
water desalination. A cascaded forward neural network (CFNN) was also developed for
58
predicting the productivity of the distillation. The result was that the CFNN had more
59
accurate productivity results than the methods of root mean square error (RMSE), mean
60
absolute percentage error (MAPE) and mean bias error (MBE). Kabeel et al. (2018) 2
ACCEPTED MANUSCRIPT 61
experimentally studied graphite in the basin of a solar still. The dimensions of the solar still
62
was 112cm×76cm. The result was that the solar still with graphite sheet gives a yield of 7.73
63
l/m2/day, which is higher than that of the conventional solar still (4.41 l/m2/day). Kabeel et
64
al. (2017) experimentally studied the modified pyramid type solar still with phase change
65
material in the v-corrugated absorber. Two identical solar stills are designed and constructed
66
for experiments. The result concluded that the PCM equipped v-corrugated absorber solar
67
still demonstrates a productivity of 6.6 l/m2/day versus a conventional pyramid solar still of
68
3.5 l/m2/day.
69
Velmurugan et al. (2008) conducted experiments in a single basin solar still with
70
sponge cubes, a wick and fins. In this work, 450 sponges of dimensions 20 mm×35 mm×35
71
mm were used. Also five fins with the dimensions of 35 mm×900 mm×1 mm were used in
72
the basin. The results showed that the solar still with fins enhanced the productivity. Kannan
73
et al. (2014) studied a solar absorption still with different absorbing materials in the basin.
74
The materials used were sponges, gravel, sand, and black rubber pieces. The results showed
75
that the combination of vapor absorption solar still with sponge, sand, and black rubber
76
pieces enhanced the system productivity. Samuel et al. (2016) conducted experiments on a
77
solar still with low cost energy storage materials. The absorbing materials used were spheres
78
and different colored sponges. Each sphere was filled with 127 g of rock salt. The test results
79
showed that the solar still with spheres enhanced the system performance and gave the
80
highest productivity of 3.7 kg/m2/day.
81
An innovative desalination technique was Ghasemi et al. (2014) experimentally
82
testing a double layer structure with bubble-wrap (BW) insulation to enhance steam
83
generation under concentrated solar illumination of 10 kW/m2. They used an exfoliated
84
graphite layer of thickness 5 mm placed on carbon foam of 10 mm thickness. Both graphite
85
and carbon foams are hydrophilic in nature to promote capillary rise of water to the top
86
surface. The result showed that the combination of graphite layer and carbon foam yields
87
solar thermal conversion efficiency of 85%, while generating steam in open air. Sharshir et
88
al. (2017) experimentally studied a modified single slope solar still with graphite flakes in
89
the basin. The modifications were graphite nano particles, phase change materials and top
90
cover cooling. Three identical solar stills were designed and tested in the same climatic
91
conditions. The results show that the combined effect of graphite flakes, phase change 3
ACCEPTED MANUSCRIPT 92
materials and cover cooling enhanced the system productivity by 73.8%. Dev et al. (2011)
93
studied an inverted absorber solar still that directs sunlight to the underside of the water
94
basin. This has the advantage of the sunlight not heating the clear cover with its absorption as
95
in a simple still. This author also studied a single slope solar still, and for both stills varied
96
water depths and total dissolved solids. The results show that the inverted absorber enhanced
97
the solar still productivity.
98
Sathyamurthy et al. (2017) reviewed the integration of collectors into various solar
99
still designs to augment the productivity. The top cover cooling effects of different solar still
100
designs were reviewed by Omara et al. (2017). Different water and air flow cooling
101
techniques were investigated. Based on the validation, the air flow and water flow over the
102
tubular and single slope solar still (SSSS) enhanced the productivity. The flow of water/air
103
affects the glass cover temperature and increases the temperature difference (Tw-Tg). Kabeel
104
et al. (2017) reviewed the three important heat exchange enhancements in solar stills. They
105
are (1) heat transfer through PCM, (2) different absorbing materials and (3) cooling
106
techniques on the top cover.
107
Mahian et al. (2017) experimentally studied a solar still with SiO2 and Cu water based
108
nanofluids. Two identical flat plate collectors (FPCs) were connected with a SSSS’s heat
109
exchanger in series mode. After heating, a pump moved the nano fluids into the SSSS via
110
pipes to enhance the heat transfer as well as productivity. Two different size of nanoparticles
111
(7 nm and 40 nm), two depths of basin water (4 cm and 8 cm) and two mass flow rates (0.04
112
kg/s and 0.12 kg/s) were examined. A mathematical model was also developed and validated
113
with experimental results. It was found that the Cu water based nanofluids had higher
114
evaporation rate than SiO2 nanofluids. Vinothkumar and Kasturi Bai (2008) experimentally
115
studied a SSSS for tap water and sea water distillation. The physical and chemical water
116
quality test results were that the water quality were compliant with the United States
117
Environmental Protection Agency (EPA) standard.
118
Many researchers tested solar stills with different absorbing materials. Absorbing
119
materials play a significant role in increasing the evaporation surface area as well as basin
120
internal thermal storage. Examples include solar stills with dye in the basin conducted by
121
Sodha et al. (1980); Dutt et al. (1989) studied wick on the basin, Minasian and Al-karaghouli
122
(1995); Shukla and Sorayan (2005); Janarthanan et al. (2005); Rajaseenivasan et al. (2015); 4
ACCEPTED MANUSCRIPT 123
Kabeel (2009); Sakthivel et al. (2010); Srivastava and Agrawal (2013); El-Sebaii and
124
Shalaby (2015); Janarthanan et al. (2006); Hansen et al. (2015), charcoal pieces, Okeke et
125
al. (1990), rubber scraps by Al-Sulttani et al. (2017), internal reflectors, Estahbanti et al.
126
(2016); Hiroshi (2011), sponge cubes Hijleh et al. (2003); Arjunan et al. (2011); Bhardwaj et
127
al. (2015), porous basin Madani and Zaki (1995), nano composite energy storage
128
Elfasakhany (2016) and presence of baffles El-Sebaii (2006); Ravishankar et al. (2015).
129
Setoodeh et al. (2011) studied the heat transfer coefficient of a solar still using computational
130
fluid dynamics (CFD). The result were that the simulated results were in good agreement
131
with experiments. Khare et al. (2017) investigated the performance of a single slope solar
132
still using CFD. The simulation result of water temperature and productivity was in
133
agreement with the experiments.
134
The present paper is the first time that recyclable BW has been used as an insulation
135
material for a solar still. BW insulation is a very good insulator due to presence of small air
136
pockets. For future work, BW could be a good insulation material for other low temperature
137
solar thermal applications. Carbon impregnated foam (CIF) can be manufactured with a
138
polyurethane open pore foam that has carbon particles coating the interior surfaces. In the
139
present work, CIFs are tested in a SSSS with BW as an insulating material. The temperature
140
distribution of the floating absorber is investigated with a CFD analysis. Based on the review
141
of various solar still designs, the testing of a solar still with BW insulation had not been
142
conducted before (the above cited BW study was for steam production). In this experimental
143
work, four identical solar stills were constructed and tested under the same climatic
144
conditions. Three modes of operation were studied experimentally: (i) SSSS without
145
insulation, (ii) SSSS with BW, and (iii) SSSS-CIF with BW. The results are compared with a
146
conventional solar still (CSS) with sawdust insulation (Mohamad et al. 1995) and
147
conclusions are drawn.
148 149
2. Materials and Methods
150
The solar stills were designed and tested at the Institute for Energy Studies, Anna
151
University, Chennai, India during the month of April to June, 2017. Four SSSSs of
152
horizontal dimensions 0.71 m × 0.71 m were designed. The material used for the making of
153
solar still is galvanized iron and coated with black paint (solar absorptivity αb ~0.95). The 5
ACCEPTED MANUSCRIPT 154
SSSS was initialized at 3 cm water depth each morning. The cover material was glass (3 mm
155
thickness, αg=0.05, and εg=0.94), and its hydrophilic property prevented distilled water from
156
falling back into the basin. It is not advisable to pour the saline water by opening the top
157
cover and closing it again because there would be significant radiative, convective, and
158
evaporative losses. Therefore, a fill port was used instead. Four pieces of CIFs floated on the
159
water surface to increase the evaporation area of the basin. The details of the foam absorber
160
are shown in Fig. 1. Fig. 2 (a-c) shows photographic views of the foam absorbers (a) top
161
view, (b) side view and (c) zoomed-in view. Generally, CIFs are used in water purifiers and
162
fish tank filters. The radius of the CIFs is 0.085 m. The total volume of the four CIFs is 1028
163
cm3 (See Table 1). The sides and bottom of the SSSS walls are properly insulated with BW
164
(Ghasemi et al. 2014) of thickness 30 mm (Khalifa and Hamood 2009). The visible
165
transmittance of the BW sheet was 80% (Ni et al. 2016). The thermocouples were placed at
166
representative places in the solar stills to record the temperature of the various segments. The
167
parameters including water temperature (Tw), internal air temperature (Tair), inner cover
168
temperature (Tic), and carbon impregnated foam temperature (TCIF) are measured with PT-
169
100 (RTD sensing devices) with an accuracy of ±0.1°C. The HP-Agilent 34970A, Data
170
Acquisition System (DAS) with an accuracy of ±1°C was used to record and log the solar
171
radiation (Pyranometer- HUKSEFLUX CP02), at a scanning rate of 1 minute throughout the
172
experiment (Fig. 3). The wind velocity was measured by using a digital anemometer (AVM-
173
03) of accuracy ±2%. A total dissolved solids (TDS) meter (TDS-3 & ±2%), electrical
174
conductivity (EC) meter (VKTECH & ±2%), and pH meter (Hanna pH & ±0.1pH) were used
175
to test the water quality from the solar still. A digital weighing balance (Healthsense, ±0.1kg)
176
was used to calculate the water holding capacity of foams and sponge. Table. 2 summarizes
177
the list of instruments used and their accuracy values. A plastic rectangular strip of length of
178
0.75 m was used to collect the condensed water on the inner glass cover. Four clean
179
BorosilTM measuring jars were used to collect the fresh water from the strip. At the end of
180
each day, the top covers of the solar stills were wiped clean with PVA sponges. The
181
schematic view of the four solar still designs is shown in Fig. 4 (A-D). The BW insulation
182
wrap over the solar still (top and bottom) is shown in Fig. 5 (a-b). Fig. 6 shows the pictorial
183
view of the SSSS designs on the open terrace. A view of the foam absorber in the solar still is
184
shown in Fig. 7 (a-c). 6
ACCEPTED MANUSCRIPT 185 186
3. Mathematical model
187
The following steps outline the simulation of the CIF in the solar still. Here, the
188
steady state temperature distribution of the CIF is studied with an energy equation. The
189
continuity equations and momentum equations are neglected because there is no flow in the
190
CIF absorber.
191 192
3.1. Energy equation
193
( E ) .keff T S h t
194
where ρ is the density, keff is the effective conductivity and Sh is the heat source.
(1)
195 196
3.2 Boundary and initial conditions
197
The side walls were assumed to be adiabatic; hence no heat losses occur in solar still to
198
ambient (See Table 3). In addition there is no leakage in the system. The physical properties
199
of solids, and liquids such as specific heat, thermal conductivity and density were taken as
200
constant. Further assumptions included that there is no temperature gradient across the basin
201
water and glass cover of the solar still. A grid independence study has been performed and
202
analyzed. The convergence criteria for the computational solution are determined and set as
203
10-6 for the governing equations.
204
The radiative heat transfer from CIF to glass is given by Setoodeh et al. (2011)
205
hr ,CIF CIF . (TCIF 273) 2 (Tg 273) 2 TCIF Tg 546
206
Note that hr radiation heat transfer coefficient (W/m2K), ε is the emissivity, σ is the Stefan-
207
Boltzmann constant (5.670×10-8W/m2 K4), T is the temperature of CIF (°C), and Tg is the
208
glass cover temperature (°C).
209
Where
CIF 210
1
g
1
CIF
(2)
1
211
Heat gained by the CIF is given in the equation by
212
mCIF C p CIF .
dTCIF I CIF g ACIF qloss qr ,CIF g dt
(3) 7
ACCEPTED MANUSCRIPT 213
Note that mCIF is the mass of the floating absorber, Cp is specific heat capacity, T is
214
temperature (°C), q is the heat transfer coefficient (W/m2K), α is the CIF absorptivity, τ is the
215 216
transmissivity of glass, and ACIF is the area of the CIF. The convective heat transfer coefficient between water and glass is estimated as, Tw 273.15 pw pg 0.884 Tw Tg 268900 pw
1/3
217 218
hc , w g
The evaporative heat transfer coefficient between water and glass is given as
219
Setoodeh et al. (2011) ,
220
Pw Pg he , w g 16.27 103 hc , w g Tw Tg
221
222 223 224
(4)
(5)
Where pw e
pg e
5144 25.314 Tw 273.15
5144 25.314 T 273.15 g
Where Pw and Pg are partial pressure of water and glass (N/m2).
225 226
4. Tested water quality analysis
227
The water quality was tested in situ. Three important parameters including TDS
228
(ppm), electrical conductivity (μS/cm) and pH were tested. The tap water is feed in to the
229
solar still (Feilizadeh et al. 2011). The water samples were collected before and after
230
treatment from the solar still and the results are shown in Table. 4. A TDS meter, pH meter
231
and EC meter were used to test the water samples instantly. Before desalination, the level of
232
TDS was 927 ppm. After desalination, it was reduced to 10 ppm (Arunkumar et al. 2012)
233
Before treatment, the level of EC was 867 μS/cm. After treatment, it was reduced to
234
34μS/cm. The level of pH before and after treatment was 6.4 and 7.4, respectively. The rain
235
water samples were collected on 16 June 2017 in a clean measuring jar. The TDS, EC and
236
pH of the tested rain water samples were 36 ppm, 16 μS/cm and 6.5. The tested results of
237
desalinated sample and rain water sample are acceptable for drinking (Samuel et al. 2016).
238
8
ACCEPTED MANUSCRIPT 239
5. Results and Discussion
240
The experimental part of this study includes solar radiation, ambient temperature,
241
temperature records in the still, CFD analysis, water-holding capacity of materials and fresh
242
water productivity.
243 244
5.1 Effect of climatic conditions
245
Fig. 8 shows the variation of solar radiation and ambient temperature with respect to
246
time. The fresh water productivity of any solar desalination unit depends upon the solar
247
radiation and ambient temperature. The highest recorded solar radiation over the tilted solar
248
still and ambient temperature (on 2017.06.02) were 842 W/m2 and 41.7°C, respectively. The
249
average solar insolation for Chennai (13.0821°N Latitude & 80.2702°E Longitude) is good
250
from February to May (See Appendix 1). The 13° South inclined top cover directly faces the
251
sun at solar noon on March 21. In Chennai, the sun position in the sky at solar noon varies
252
from 36.45° South to 10.45° North in Dec 21 and June 21, respectively. As far as the solar
253
radiation over the tilted surface is concerned, the best time to conduct the experiment should
254
be from February to April. But on the other hand, due to greater day length from March-
255
June (See Appendix 2), it is better to perform the experiment in these months. The higher
256
the direct solar radiation is, the higher the yield is (Sahota et al. 2017). Although June has the
257
greatest day length, due to clouds, the average intensity of solar radiation is less. It is
258
concluded from our observation that the best time to perform the desalination experiment in
259
Chennai is from March to May. The wind conditions were also recorded during the
260
experiment. There are many factors that affect the solar stills productivity such as water
261
depth, thickness of the glass, height of the walls, and angle of inclination. The effect of
262
ambient temperature and wind also plays a significant role in the productivity.
263
5.2 Variation of recorded solar still temperature
264
Fig. 9 (a) shows the results of measured water temperature (Tw), internal air
265
temperature (Tair), and inner cover temperature (Tic) of SSSS without insulation (See Table.5)
266
The recorded maximum of Tw, Tair, and Tic are 59.1°C, 55.5°C, and 50.5°C, respectively. Fig.
267
9 (b) shows the measured temperature profile of SSSS with BW insulation (See Table 6).
268
The maximum recorded temperatures of Tw, Tair, and Tic are 70.3°C, 69°C, and 65.7°C,
269
respectively. Fig. 9 (c) shows the variation of Tw, Tair, Tic, and TCIF of SSSS-CIF with BW 9
ACCEPTED MANUSCRIPT 270
insulation (See Table 7). The maximum reached Tw and TCIF are 70.4°C & 71.9°C. Fig. 9 (d)
271
shows the temperature variations of CSS with wooden insulation (See Table 8). The recorded
272
maximum of Tw, Tair, and Tic are 68.7°C, 66°C, and 60°C, respectively. Based on the results
273
of all the experiments, the SSSS-CIF with BW insulation shows the highest temperature. The
274
recorded temperature profile of the conventional single slope solar still for similar ambient
275
conditions, area and with wooden insulation is shown in Fig. 9(d). It clearly shows that the
276
solar still with insulation increase the temperature of water by 23% as compared to solar still
277
without insulation as the loss of heat from the basin to the surrounding is reduced.
278
The hourly variation in evaporative heat transfer coefficient (hew) for the tested
279
configurations is shown in Fig 10. The evaporative heat transfer coefficient is calculated
280
using Equation (4) and (5). It can be observed that the solar still without any kind of
281
insulation has ~1/3 lower evaporative coefficient inside the basin as compared to solar still
282
with insulation and CIF porous medium. A maximum of 47.5 W/m2K evaporative heat
283
transfer coefficient is observed in the case of solar still with CIF and bubble wrap insulation.
284
5.3 CFD simulation results
285
The CFD analysis was carried out using ANSYS Fluent 15.0. The mesh geometry of
286
the CIF is shown in Fig. 11. The simulation of the floating absorber temperature distribution
287
is predicted by using CFD analysis (Fig. 12). The major objective of this CFD simulation is
288
to analyze the temperature distribution on the floating absorber. The time taken to complete
289
the simulation process is 4-5 hours. The parameters used to solve the temperature distribution
290
on the foam are given in Table. 9. The experimental and simulation result of maximum
291
recorded floating absorber temperature is 71.5°C and 73°C, respectively. The temperature
292
profiles of the CIFs are investigated with CFD analysis and the simulation results show good
293
agreement with the measured result.
294
5.4 Fresh water productivity in the solar stills
295
Fig. 13 shows the fresh water productivity of solar still designs correlated with solar
296
radiation. The productivity of the SSSS without insulation, SSSS with BW insulation, SSSS-
297
CIF with BW insulation and CSS with sawdust insulation are 1.9 l/m2/day, 2.3 l/m2/day, 3.1
298
l/m2/day and 2.2 l/m2/day, respectively. The SSSS-BW insulation shows a slight
299
enhancement over the CSS with wooden insulation. Normally, a wooden frame with glass
300
wool or sawdust insulation is traditionally used in SSSS. But some factors compromise the 10
ACCEPTED MANUSCRIPT 301
wooden frame and sawdust insulation. They include (i) basin leakage, (ii) leakage in fresh
302
water channel and (iii) excessive precipitation if the system is not sealed adequately.
303
5.5 Effect of BW and floating absorber
304
The BW is nothing more than pockets of air wrapped in polymer. The air inside a
305
confined space acts as a poor conductor of heat, which in turn reduces heat loss to
306
surroundings. The air inside a confined space inhibits convection. Here, the SSSS is tightly
307
packed with BW of thickness 30 mm to reduce the heat loss. Due to the heat trapped by the
308
BW insulation, Tw, Tair, and Tic and are the maximum for all the configurations. If the
309
temperature difference (∆T) between Tw and Tic is lower, this causes a decrease in
310
productivity (Arunkumar et al. 2012). The hydrophilic interconnected CIFs occupied a
311
surface area of 0.214 m2 in the 0.50 m2 basin. The advantages of the CIFs are: (i) acting as an
312
internal heat storage element, and (ii) increasing the evaporation area of the basin. The
313
interconnected CIFs consist of a large quantity of air out of the water, so their thermal
314
conductivity is low there. However, in the water, because they are hydrophilic, they fill with
315
water. Still, because it is difficult for the water to move in the pores, the thermal conductivity
316
is lower than free water. This coupled with the solar absorption increases the temperature on
317
the top side of the CIFs. The SSSS is an airtight container. The interconnected CIFs float on
318
the water surface and they increase the evaporation (the hydrophilic nature allows the
319
capillary flow of water from bottom to spreading out over the top side for ease of
320
evaporation). The water vapor condenses on the inner glass cover and trickles down due to
321
gravity. Because the CIF is hydrophilic, the wetted surface area increases above that of open
322
water (Ghasemi et al. 2014). This increases the evaporation rate, enhancing the productivity.
323
5.6 Effect of water holding capacity of foams and sponge
324
Table. 10 show the comparison of water-holding capacity of polyurethane foams,
325
PVA sponges and CIFs (Figs.14-15). Sponges are made with many holes connected
326
throughout (open pore) to hold lot of water for various applications. The air portions are
327
replaced by water when the sponges contact a water surface. Due to their hydrophilic nature,
328
the water quickly spreads throughout the sponge. The tested results of water holding capacity
329
reveals that the PVA sponge can hold more water per dry mass than the other materials. The
330
PVA sponge is physically hard when dry and becomes soft when it gets wet. Carbon foams
331
are as good at holding water. The behavior of the CIF and sponge are interesting in the 11
ACCEPTED MANUSCRIPT 332
presence of solar radiation. The top surface of the sponges seems to be dry even as it is
333
saturated with water. Therefore, more energy is needed to evaporate the water from the
334
inside of the sponge cubes. In CIFs, the structural arrangement is such that the top is wet
335
when placed in water. This shows than the CIF allows fluid movement from the bottom to
336
the top surface. So the CIFs help to ease evaporation of water and pave a path to more fresh
337
water production.
338
5.7 Cost Comparison
339
The cost of the SSSS-CIF with BW insulation is shown in Table. 11. The overall
340
assumptions are a device life of 15 years, an equivalent of 80% sunny days, and an interest
341
rate of 6%. The total cost of the fabricated solar still without insulation would have been
342
approximately 34 USD for 1 m2. With an output of 1.92 l/m2/day, this is approximately
343
0.0060 $/l water, the baseline. Adding plywood insulation increased cost by 60%, but only
344
increased output by 10%, so the water was 0.0086 $/l, which is worse than baseline. On the
345
other hand, adding BW insulation increased cost by only 5%, but increased output by 22%,
346
so the water was 0.0051 $/l, an improvement from the baseline. Finally, adding both BW
347
insulation and the CIF increased cost of the baseline by 62%, but only increased output by
348
37%, so the water was 0.0064 $/l. Therefore, the minimum cost water was produced by the
349
BW insulation without the CIF absorber.
350 351
6. Comparison of previous results with present work
352
The comparisons of different insulation materials used by the researchers are shown
353
in Table. 12. The effect of insulation thickness on the productivity is studied by Khalifa and
354
Hamood (2009). They maintained three different insulation thicknesses of 30 mm, 60 mm
355
and 100 mm. The results were that the insulation thickness plays a significant role in the
356
productivity up to a thickness of 60 mm. From the detailed review of previous results,
357
sawdust (0.08 W/m.K), glass wool (0.04 W/m.K) and plywood (0.13W/m.K) are widely used
358
in solar stills to reduce the heat loss to surroundings. Denkenberger and Pearce concluded via
359
modeling that varying the insulation thermal resistance from 1 to 4 ºC/(W/m2) changed
360
output 19% (Pearce et al. 2016). The advantages of the BW (0.02 W/m.K) insulation are low
361
cost (1 m2~0.23$) and that it is easy to wrap around the unit. The BW insulation acted as a
362
water proof layer for the solar still during rainy days. Based on the comparisons, BW 12
ACCEPTED MANUSCRIPT 363
insulation in a SSSS moderately increases the productivity of solar still, but there could
364
easily be confounding factors. Fig. 16 shows the cost per litre (CPL) of previous results
365
(Rajaseenivasan and Murugavel 2013); (El-Agouz 2014); (Omara et al. 2011); (Abdullah and
366
Badran 2008); (Ansari et al. 2013); (Fath et al. 2003); (Wassouf et al. 2011); (Suneesh et al.
367
2014); (Kabeel 2009) with single slope solar stills. It is concluded from the chart that all of
368
the embodiments tested in this paper were lower distilled water cost than previous work. The
369
lowest cost of water was with BW and no foam absorber.
370 371
7. Conclusions
372
The effect of floating absorbers and BW insulation on the SSSS is experimentally
373
tested under Indian climatic conditions. Four identical solar stills are designed and tested in
374
the same environment to reach a concrete conclusion. Three modes of operation were studied
375
experimentally: (i) SSSS without insulation, (ii) SSSS with BW insulation, and (iii) SSSS-
376
CIF with BW. The 4 pieces of CIF are floated on the water surface. The results are compared
377
with a CSS with sawdust insulation.
378 379
The temperature profiles of the CIFs are investigated with CFD analysis and the simulation results show good agreement with the measured result.
380
The productivities of the SSSS without insulation, SSSS with BW insulation, SSSS-
381
CIF with BW insulation, and CSS were 1.9 l/m2/day, 2.3 l/m2/day, 3.1 l/m2/day and
382
2.2 l/m2/day respectively.
383 384
The combination of internal heat storage (CIF) and heat trap (BW) yields superior performance.
385
The BW insulation enhanced the productivity by 22% over solar still without
386
insulation. The SSSS-BW-CIF combination increased the productivity of 24% over
387
SSSS with BW insulation. The SSSS with BW insulation enhanced the productivity
388
of 10% over the SSSS with wooden insulation.
389
The hydrophilic nature and interconnected carbon impregnated absorbers enhanced
390
fresh water productivity in the SSSS. The foams increase the evaporation surface area
391
of the basin.
13
ACCEPTED MANUSCRIPT 392
Preliminary water quality tests were conducted and the results are in the acceptable
393
range suggested by the World Health Organization (WHO) and the Indian standard
394
specification.
395 396 397 398
The pockets of air in the BW act as a poor thermal conductor and restrict the heat loss to surroundings. This is easier to use than other traditional alternatives. Solar desalination is a low global warming impact method of producing safe drinking water.
399 400
8. Implications for theory and practice of cleaner production/sustainability
401
In remote areas and regions, fresh water is often trucked in. This consumes finite fossil fuels
402
and produces greenhouse gases. A much cleaner way of producing freshwater is with solar
403
energy. A promising way of doing this is with solar stills. This paper shows a promising new
404
technique to increase the productivity of solar stills.
405 406 407 408 409 410 411 412
9. Future work The evaporative heat transfer from solar still as well as CIF could be simulated by using CFD analysis. Graphite flakes (GF) could be used to form a layer on the CIF to increase the thermal conductivity. Selective Copper Oxide coating could be applied on the top of CIF to reduce radiation loss and increase temperature of the foam segment.
413 414 415 416 417 418 419 420 421 422 14
ACCEPTED MANUSCRIPT 423
Appendix 1
424
Incident angle of beam radiation over the 13° south tilted glazing cos sin sin .cos cos .cos .cos .sin cos cos .cos .cos sin .cos .sin
425
(A)
cos .sin .sin .sin 426
Where θ is the incidence angle (°), ϕ is the latitude in (°), δ is the declination angle (°), γ is
427
the surface azimuth angle(°) and ω is the hour angle (°)South facing glazing angle, γ=0,
428
Incidence angle at solar noon, ω = 0
429
Then Equation (A) becomes,
430
cos sin .sin cos .cos
431
Since ϕ=β=13°, Eq. (B) becomes,
432
cos cos
433
Declination angle,
434
23.45sin
435
Where δ is the declination angle (°) and n is the number of days in the year
(B)
(C) 360 (284 n) 365
(D)
February 22
March 22
April 22
n=53
n=80
n=112
δ=-10.87°
δ=0°
δ=11.93°
From Eq. (B), θ=10.87°
From Eq. (B), θ=0°
From Eq. (B), θ=11.93°
436 437
Angle made by the beam radiation with the normal to the glazing surface at noon are 10.87°,
438
0° and 11.93° on Feb 22, April 22 and March 22 respectively. It clearly shows that on March
439
22, the solar beam radiation at the noon will be normal to the tilted glazing.
440 441 442 443 444 445 446 15
ACCEPTED MANUSCRIPT 447
Appendix 2
448
Day length calculation for March 22-June 22 and Dec 22.
449
Hour angle s cos 1 ( tan .tan )
450
Where ωs is the hour angle corresponds to sunrise or sunset, ϕ is the latitude in (°) and δ is
451
the declination angle (°).
452
23.45sin
453
Day length (DL)= DL
(E)
360 (284 n) 365 2 s 15
(F)
March 22
April 22
May 22
June 22
July 22
December 22
n=81
n=112
n=142
n=173
n=203
n=356
By Eq. (D),
By Eq. (D),
By
By Eq. (D),
By Eq. (D),
δ=0°
δ=11.93°
δ=20.34°
δ=23.45°
δ=20.24°
δ=-23.45°
By Eq. (E),
By Eq. (E),
By Eq.(E),
By Eq.(E),
By Eq.(E),
By Eq.(E),
ωs=90°
ωs=92.79°
ωs=94.91°
ωs=95.75°
ωs=94.88°
ωs=84.25°
By Eq.(F),
By Eq.(F),
By Eq.(F),
By Eq.(F),
By Eq.(F),
By Eq.(F),
DL=12 h
DL= 12 h &
DL=12 h & 39
DL= 12 h & DL= 12 h & DL= 11 h &
22 min
min
45 min
Eq.
(D), By Eq. (D),
39 min
14 min
454 455
By calculation, it is clear that the day length will increase up to a maximum of 12 hours
456
45min on June 22 and further it will decrease. A minimum day length of 11 h 14 min is
457
calculated for December 22.
458 459 460 461 462 463 464 465 466 16
ACCEPTED MANUSCRIPT 467
10. Nomenclature
468
A
-
Area (m2)
469
Cp
-
Specific heat capacity (J/kg.K)
470
E
-
Energy (J)
471
h
-
Heat transfer coefficient (W/m2K)
472
I(t)
-
Incident solar radiation (W/m2)
473
k
-
Thermal conductivity (W/m.K)
474
L
-
Latent heat of vaporization (J/kg)
475
m
-
mass (kg)
476
P
-
Partial pressure (N/m2)
477
n
-
number of days
478
T
-
Temperature (°C)
479
V
-
Wind velocity (m/s)
480
q
-
heat transfer coefficient (W/m2.K)
481 482
Greek
483
α
-
Absorptivity
484
μ
-
Viscosity (kg/m/s)
485
ε
-
Emissivity
486
ρ
-
Density (kg/m3)
487
σ
-
Stefan-Boltzmann constant = 5.67×10-8 W/m2K4
488
τ
-
solar transmittance of glazing
489
∆
-
temperature difference
490
θ
-
incidence angle (°),
491
ϕ
-
latitude in (°),
492
δ
-
declination angle (°),
493
γ
-
surface azimuth angle(°),
494
ω
-
hour angle (°)
495 496 497
Subscripts 17
ACCEPTED MANUSCRIPT 498
amb
-
ambient
499
air
-
internal air
500
b
-
basin
501
c
-
convection
502
CIF
-
carbon impregnated foam
503
e
-
evaporation
504
eff
-
effective
505
g
-
glass
506
ic
-
inner cover
507
loss
-
loss
508
r
-
radiation
509
s
-
sunrise or sunset
510
w
-
water
511 512
Abbreviation
513
BW
-
Bubble-wrap
514
CFM
-
Cubic foot/minute
515
CPC
-
Compound parabolic concentrator
516
CPL
-
Cost per litre
517
CIF
-
Carbon impregnated foam
518
CSS
-
Conventional solar still
519
CFD
-
Computational fluid dynamics
520
DAS
-
Data acquisition system
521
DL
-
Day length
522
EC
-
Electrical conductivity (μS/cm)
523
GF
-
Graphite flake
524
PPI
-
Pores per inch
525
PVA
-
Polyvinyl Alcohol
526
RTD
-
Resistance temperature detector
527
SSSS
-
Single slope solar still
528
TDS
-
Total dissolved solids (ppm) 18
ACCEPTED MANUSCRIPT 529 530 531
11. Acknowledgement
532
This study received grant from University Grant Commission (UGC), Government of
533
India. Ref. No. F.4-2/2016 (BSR)/PH/14-15/0124 dated on 01 July 2016.
534 535 536
12. References
537 538 539 540 541
Abdullah, S., Badran, O.O., 2008. Sun tracking system for productivity enhancement of solar still. Desalination 220,669-676. Abu–Hijleh, B.A.K., Hamzeh M. Rababa'h., 2003. Experimental study of a solar still with sponge cubes in basin. Energ. Convers. Manag. 44,1411-1418.
542
Achmad Chafidz., Esa D. Kerme., Irfan Wazeer., Yasir Khalid., Abdelhamid Ajbar., Saeed
543
M. Al-Zahrani., 2016. Design and fabrication of a portable and hybrid solar-powered
544
membrane distillation system. J Clean. Prod. 133, 631-647.
545
Ali O. Al-Sulttani., Amimul Ahsan., Ammar N. Hanoon., Rahman, A., Idrus, S., 2017.
546
Hourly yield prediction of a double-slope solar still hybrid with rubber scrapers in low-
547
latitude areas based on the particle swarm optimization technique. Appl. Energy
548
203,280-303.
549 550
Ansari, O., Asbik, M., Abdullah Bah., Arbaoui, A., 2013. Desalination of brackish water using passive solar still with a heat energy storage system. Desalination 324,10-20.
551
Arjunan, T.V., Aybar, H.Ş., Nedunchezihan, N., 2011. Effect of sponge liner on the internal
552
heat transfer coefficients in a simple solar still. Desalin. Water Treat. 29,271-284.
553
Arunkumar, T., Jayaprakash, R., Amimul Ahsan., Denkenberger, D.C., Okundamiya, M.S.,
554
Sanjay Kumar., Aybar, H.Ş., 2012. An experimental study on hemispherical solar still.
555
Desalination 286,342-348.
556
Arunkumar, T., Velraj, R., Denkenberger, D., Ravishankar Sathyamurthy., Vinothkumar K.,
557
Porkumaran, K., Amimul Ahsan., 2016. Effect of heat removal on tubular solar
558
desalting system. Desalination 379,24-33. 19
ACCEPTED MANUSCRIPT 559
Arunkumar, T., Velraj. R., Denkenberger, D., Ravishankar Sathyamurthy., 2016. Influence
560
of crescent shaped absorber in water desalting system. Desalination 398,208-213.
561
Ashraj Elfasakhany., 2016. Performance assessment and productivity of a simple-type solar
562
still integrated with nano composite energy storage system. Appl. Energy 183,399-
563
407.
564 565
Bashart Jamil., Naiem Akhtar., 2017. Effect of specific height on the performance of a single slope solar still: An experimental study. Desalination 414,73-78.
566
Bhardwaj, R., ten Kortenaar, M.V., Mudde, R.F., 2015. Maximized production of water by
567
increasing area of condensation surface for solar distillation. Appl. Energy 154,480-
568
490.
569
Bhupendra
Gupta.,
Raghvendra
Sharma.,
Prem
Shankar.,
Prashant
Baredar.,
570
2016.Performance enhancement of modified solar still suing a water sprinkler: An
571
experimental approach. Perspectives in Science 8,191-194.
572 573 574 575 576 577 578 579
Dutt. D.K., Ashok Kumar., Anand, J.D., Tiwari, G.N., 1989. Performance of a double-basin solar still in the presence of dye. Appl. Energy 32,207-223. El-Agouz S.A., 2014. Experimental investigation of stepped solar still with continuous water circulation. Energ. Convers. Manage. 86,186-193. El-Sebaii, A.A., Aboul-Enein, S., El-Bialy, E., 2006. Single basin solar still baffle suspended absorber. Energ. Convers. Manag. 41,661-675. El-Sebaii, A.A., Shalaby, S.M., 2015. Parametric study and heat transfer mechanisms of single basin v-corrugated solar still. Desalin. Water Treat. 55,285-296.
580
Fath, H.E.S., El-Samanoudy, M., Fahmy, K., Hassabou, A., 2003. Thermal economic
581
analysis and comparison between pyramid-shaped and single-slope solar still
582
configurations. Desalination 159,69-79.
583
George Ni., Gabriel Li., Svetlana V. Boriskina., Hongxia Li., Weilin Yang., TieJun Zhang,
584
Gang Chen., 2016. Steam generation under one sun enabled by a floating structure
585
with thermal concentration. Nature Energy DOI: 10.1038/NENERGY.2016.126.
586
Hadi Ghasemi., George Ni., Amy Marie Marconnet., James Loomis., Selcuk Yerci., Nenad
587
Miljkovic., Gang Chen., 2014. Solar steam generation by heat localization. Nat.
588
Commun. doi: 10.1038/ncomms5449. 20
ACCEPTED MANUSCRIPT 589
Harris Samuel, D.G., Nagarajan, P.K., Ravishankar Sathyamurthy., El-Agouz S.A., Kannan,
590
E., 2016. Improving the yield of fresh water in conventional solar still using low cost
591
energy storage material. Energ. Convers. Manag. 112,125-134.
592
Janarthanan, B., Chandrasekaran, J., Kumar, S.,
2005. Evaporative heat loss and heat
593
transfer for open- and closed-cycle systems of a floating tilted wick solar still.
594
Desalination 180,291-305.
595
Janarthanan, B., Chandrasekaran, J., Kumar, S., 2006. Performance of floating cum tilted-
596
wick type solar still with the effect of water flowing over the glass cover. Desalination
597
190,51-62.
598
Joe Partrik Gnanaraj, S., Ramachandran, S., David Santhosh Christopher., 2017. Enhancing
599
the design to optimize the performance of double basin solar still. Desalination
600
411,112-123.
601 602 603 604
Kabeel, A.E., 2009. Performance of solar still with a concave wick evaporation surface. Energy 34,1504-1509. Kabeel, A.E., 2009. Performance of solar still with a concave evaporation surface. Energy 34,1504-1509.
605
Kabeel, A.E., Arunkumar, T., Denkenberger, D.C., Ravishankar Sathyamurthy., 2017.
606
Performance enhancement of solar still through efficient heat exchange mechanism- A
607
Review. Appl. Therm. Eng. 114,815-836.
608
Kabeel, A.E., Mohamed Abdelgaied., Amr Eisa., 2018. Enhancing the performance of single
609
basin solar still using high thermal conductivity sensible heat storage materials. J
610
Clean. Prod. 183, 20-25.
611
Kabeel, A.E., Mohamed A. Teamah., Mohamed Abdelgaied., Gaml B. Abdel Aziz., 2017.
612
Modified pyramid solar still with v-corrugated absorber plate and PCM as a thermal
613
storage medium. J Clean. Prod. 161, 881-887.
614
Kamel Rabhi., Rached Nciri., Faouzi Nasri., Chaouki Ali., Habib Ben Bacha., 2017.
615
Experimental performance analysis of a modified single-basin single-slope solar still
616
with pin fins absorber and condenser. Desalination 416,86-93.
617
Kannan, R., Selvaganesan, C., Vignesh, M., Ramesh Babu, B., Fuentes, M., Vivard, M.,
618
Skyrabin, I., Srithar, K., 2014. Solar still with vapor adsorption basin: Performance
619
analysis. Renew. Energy 62,258-264. 21
ACCEPTED MANUSCRIPT 620
Karimi Estahbanti., Amimul Ahsan., Mehraz Feilizadeh., Khosrow Jafarpur., Seyedeh-Saba
621
Ashrafmansouri.,
622
investigation on internal reflectors in a single-slope solar still. Appl. Energy 165,537-
623
547.
624
Mansoor
Feilizadeh.,
Khalifa, A.J.N., Ahmad M. Hamood.,
2016.
Theoretical
and
experimental
2009. Effect of insulation thickness on the
625
productivity of basin type solar stills: An experimental verification under local climate.
626
Energ. Convers. Manag. 50,2457-2461.
627
Kharpal, Arjun. Stephan Hawking says humans must colonize another plant in 100 years or
628
face extinction,http://www.cnbc.com/2017/05/05/stephen-hawking-human-extinction-
629
colonize-planet.html Accessed July 2017.
630 631 632 633
Koroneos, C., Dompros, A., Roumbas, G., 2007. Renewable energy driven desalination system and modelling. J Clean. Prod. 15, 449-464. Madani, A.A., Zaki, G.M., 1995. Yield of solar stills with porous basins. Appl. Energy 52,273-281.
634
Manssor Feilizadeh., Karimi Estahbanati., Khosrow Jafarpur., Keza Roostaazad., Mehrzad
635
Feilzadeh., Hamed Taghvaei., 2015. Year-round outdoor experiments on a multi-stage
636
active solar still with different numbers of solar collectors. Appl. Energy 152,39-46.
637 638
Minasian, A.N., Al-karaghouli, A.A., 1995. An improved solar still: The wick-basin type. Energ. Convers. Manag. 36,213-217.
639
Mohamad, M.A., Soliman, S.H., Abdel-Salam., Hussein, H.M.S., 1995. Experimental and
640
financial investigation of asymmetrical solar stills with different insulation. Appl.
641
Energy 52,265-271.
642
Mohammed Shadi Abujazar, S., Suja Fatihah., Ibraahim Anwar., Kabeel, A.E., Surya Sharil.,
643
2018. Productivity modelling of a developed inclined stepped solar still system based
644
on actual performance and using a cascaded forward neural network model. J Clean.
645
Prod. 170, 147-159.
646
Muthumanokar, A., Prince Winston, D., Kabeel, A.E., Ravishankar Sathyamurthy., 2018.
647
Sustainable fresh water and power production by integrating PV panel in inclined solar
648
still. J Clean. Prod. 172, 2711-2719.
22
ACCEPTED MANUSCRIPT 649
Narjes Setoodeh., Rahbar Rahimi., Abolhasan Ameri., 2011. Modeling and determination of
650
heat transfer coefficient in a single basin solar still using CFD. Desalination 268,103-
651
110.
652 653 654 655 656 657
Okeke, C.E., Egarievwe, S.U., Animalu, A.O.E., 1990. Effects of coal and charcoal on solarstill performance. Energy 15,1071-1073. Omara, Z.M., Abdullah, A.S., Kabeel, A.E., Essa, F.A., 2017. The cooling techniques of the solar stills’ glass covers- A review. Renew. Sustain. Energy Rev. 78,176-193. Omara, Z.M., Morfreh, H., Hamed, M.H., Kabeel, A.E., 2011. Performance of finned and corrugated absorbers solar still under Egyptian conditions. Desalination 277, 281-287.
658
Omid Mahian., Ali Kianifar., Saeed Zeinali Heris., Dongsheng Wen., Ahmet Z. Sahin.,
659
Somchai Wongwises., 2017. Nanofluids effects on the evaporation rate in a solar still
660
equipped with a heat exchanger. Nano Energy 36,134-155.
661
Pankaj K. Srivastava., Agrawal, S.K., 2013. Experimental and theoretical analysis of single
662
sloped basin type solar still consisting of multiple low thermal inertia floating porous
663
absorbers. Desalination 311,198-205.
664
Pearce, Joshua M., and D.C. Denkenberger. Numerical simulation of the direct application of
665
compound parabolic concentrators to a single effect basin solar still." Proceedings of
666
the 2006 International Conference of Solar Cooking and Food Processing. Vol. 118.
667
2006.
668
pH in Drinking-water, World Health Organization 2007. Available:
669
http://www.who.int/water_sanitation_health/dwq/chemicals/ph_revised_2007_clean_v
670
ersion.pdf
671
Rahul Dev., Sabah Abdul-Wahab A., Tiwari, G.N., 2011. Performance study of the inverted
672
absorber solar still with water depth and total dissolved solids. Appl. Energy 88,252-
673
264.
674
Rajaseenivasan, T., Kalidasa Murugavel, K., Elango, T., 2015. Performance and exergy
675
analysis of a double basin solar still with different materials in the basin. Desalin.
676
Water Treat. 55,1786-1794.
677
Rajaseenivasan, T., Prakash, R., Vijayakumar, K., Srithar, K., 2017. Mathematical and
678
experimental investigation on the influence of basin height variation and stirring of
679
water by solar PV panels in solar still. Desalination 415,67-75. 23
ACCEPTED MANUSCRIPT 680 681
Rajaseenivasan. T, Murugavel K.K., 2013. Theoretical and experimental investigation on double basin double slope solar still. Desalination 319,25-32.
682
Ravishankar Sathyamurthy., El-Agouz S.A, Nagarajan P.K, Subramani, J., Arunkumar, T.,
683
Mageshbabu, D., Madhu, B., Bharathwaaj, K., Prakash, N., 2017. A review of
684
integrating solar collectors to solar still. Renew. Sustain. Energy Rev. 77,1069-1097.
685
Ravishankar Sathyamurthy., Nagarajan, P.K., El-Agouz., Jaiganesh, V., Sathish Khanna, P.,
686
2015. Experimental investigation on a semi-circular trough-absorber solar still with
687
baffles for fresh water production. Energ. Convers. Manag. 97,235-242.
688
Sakthivel, M., Shanmugasundaram, S., Alwarsamy, T., 2010. An experimental study on a
689
regenerative solar still with energy storage medium-jute cloth. Desalination 264,24-31.
690
Samuel Hansen, R., Surya Narayanan, C., Kalidasa Murugavel, K., 2015. Performance
691
analysis on inclined solar still with different new wick materials and wire mesh.
692
Desalination 358,1-8.
693
Sharshir, S.W., Guilong Peng., Lirong Wu., Essa F.A., Kabeel, A.E., Nuo Yang., 2017. The
694
effects of flak graphite nanoparticles, phase change material and film cooling on the
695
solar still performance. Appl. Energy 191,358-366.
696 697 698 699 700 701 702 703 704
Shukla, S.K., Sorayan, V.P.S., 2005. Thermal modeling of solar stills: an experimental validation. Renew. Energ. 30,683-699. Sodha, M.S., Kumar, A., Tiwari G.N., Pandey, G.C., 1980. Effect of dye on the performance of a solar still. Appl. Energy 7,147-162. Suneesh, P.U., Jayaprakash, R., Arunkumar, T., David Denkenberger., 2014. Effect of air flow on “V” type solar still with cotton gauze cooling. Desalination 337,1-5. Tanaka Hiroshi., 2011. Solar thermal collector augmented by flat plate booster reflector: Optimum inclination of collector and reflector. Appl. Energy 88,1395-1404. Tien Shiao, Andrew Maddocks, Chris Carson and Emma Loizeaudx, 3 maps explain India’s
705
growing water risks, http://www.wri.org/blog/2015/02/3-maps-explain-
706
india%E2%80%99s-growing-water-risks February 26, 2015.
707 708 709 710
Tiwari, G.N., Tiwari, A.K., Solar distillation practice for water desalination systems. Jan 2008 Total dissolved solids in Drinking-water,
World Health Organization 2003. Available:
http://www.who.int/water_sanitation_health/dwq/chemicals/tds.pdf 24
ACCEPTED MANUSCRIPT 711
Vaibhav Rai Khare., Abhay Pratap Singh., Hemant Kumar., Rahul Khatri., 2017. Modeling
712
and performance enhancement of single slope solar still using CFD. Energy Procedia
713
109,447-455.
714 715 716 717 718 719 720 721
Velmurugan, V., Gopalakrishnan, M., Raghu, R., Srithar, K., 2008. Single basin solar still with fin for enhancing productivity. Energ. Convers. Manag. 49,2602-2608. Vinoth Kumar, K., Kasturi Bai, R., 2008. Performance study on solar still with enhanced condensation. Desalination 230,51-61. Wassouf, P., Peska, T., Singh, R., Akbarzadeh, A., 2011. Novel and low cost designs of portable solar stills. Desalination 276,294-302. Water quality standards, WHO 2011, http://mrccc.org.au/wpcontent/uploads/2013/10/Water-Quality-Salinity-Standards.pdf
722 723 724 725 726 727 728 729 730 731 732 733 734 735 736 737 738 739 740 741 25
ACCEPTED MANUSCRIPT 742
Table. 1
743
Details of a single CIF S.No. Parameters
Values
1
Volume
257 cm3
2
Diameter
0.17 m
3
Thermal conductivity
0.25 W/m K
4
Pores per inch (PPI)
10-65 PPI
5
Mass
9g
6
Color
Black
744 745 Table. 2 746 Accuracy of the measuring instruments
S.No.
Instrument
Model/Make
Accuracy
Range
1
Data Acquisition System
HP-Agilent 34970A
±1°C
0-100°C
2
Pyranometer
HUKSEFLUX CP02
±5 W/m2
0-1750 W/m2
3
K-type thermocouples
GENERIC
±0.1°C
0-100°C
4
Anemometer
AVM-03
±2%
0-9990 CFM
5
Measuring jar
Borosil
±10 ml
0-1000 ml
6
TDS meter
TDS-3
±2%
0-99990 ppm
7
EC meter
VKTECH
±2%
0-99990 µS/cm
8
pH meter
Hanna pH
±0.1 pH
0.0-14 pH
9
Digital weighing balance
Healthsense
±0.1kg
1-5000 g
747 748
Table. 3
749
Boundary zone type and conditions S.No.
Zone
Zone type
Description
1
Top CIF surface
Wall
h = 10 W/m2
2
Bottom CIF surface
Wall
T = 303-344 K
3
Side CIF surface
Wall
T = 303-344 K
750 751 26
752
Table. 4
753
Tested water quality results EC TDS, ppm (WHO, 2003)
(μS/cm)
pH (WHO 2007)
Before
After
Acceptable Before
treatment treatment level 927
14
Less than 300
After
Acceptable Before
treatment treatment level 6.4
7.4
6.5-8.5
754 755 756 757 758 759 760 761 762 763 764 765 27
After
37
water
on 16.06.2017.
Acceptable
treatment treatment level 867
rain
samples are collected
(WHO 2011)
S.No.
1
Tested
0-800
TDS (ppm) 36
pH 6.5
EC (μS/cm) 16
766
Table. 5
767
Hourly variation of measured values for SSSS without insulation (2017/06/02) Sl.No.
I (W/m2)
Tamb (°C)
V (m/s)
Tw (°C)
Tair (°C)
Tic (°C)
9:00 9:30 10:00 10:30 11:00 11:30 12:00 12:30 13:00 13:30 14:00 14:30 15:00 15:30 16:00 16:30 17:00 17:30
580 650 715 754 810 844 857 855 842 806 746 672 590 494 395 308 185 135
26 26.6 34.5 35.4 36.2 36.1 36.3 36 36 36 36.4 35.2 34.5 34.8 36.3 34.5 33.7 33
1.02 2.985 0.82 3.819 3.268 2.926 0.795 2.8 1.05 1.3 2.305 1.869 1.789 1.322 2.159 1.025 3.531 2.309
34 37 41 44 46 50.5 53 55.5 57.2 58.5 59.1 55.6 51.5 49.5 47.5 45 44 42
33 35.5 40.5 43.5 46 48 51 52 55.5 55 54 52.5 49 48.6 47 44.5 43.5 41
33.5 35 36.5 39 42 43.5 46 48.5 50 50.5 50 49.5 48.5 47 45 42.5 40 39
768 769 770 771 772 28
Pd (ml/m2/day) 0 40 48 72 80 100 112 128 148 156 164 156 148 136 128 112 100 76
773
Table. 6
774
Hourly variation of measured values for SSSS with BW insulation (2017/06/02) Sl.No.
I (W/m2)
Tamb(°C)
V (m/s)
Tw (°C)
Tair (°C)
Tic (°C)
9:00 9:30 10:00 10:30 11:00 11:30 12:00 12:30 13:00 13:30 14:00 14:30 15:00 15:30 16:00 16:30 17:00 17:30
580 650 715 754 810 844 857 855 842 806 746 672 590 494 395 308 185 135
26 26.6 34.5 35.4 36.2 36.1 36.3 36 36 36 36.4 35.2 34.5 34.8 36.3 34.5 33.7 33
1.02 2.985 0.82 3.819 3.268 2.926 0.795 2.8 1.05 1.3 2.305 1.869 1.789 1.322 2.159 1.025 3.531 2.309
47.3 48.6 51.9 58.6 61.1 63.5 67.6 68.3 69.2 69.8 70.3 69.5 68.9 66.5 64.1 59.8 51.6 50
47.1 48.3 50.3 56.4 59.4 62.1 65 66.4 66.9 67.8 69 68.3 67.8 66.3 63.9 60.2 56.4 55
46 47.8 49.3 54.8 56.5 58.5 60.6 62.8 63.3 64.7 65.7 63.9 62.2 60.2 59.9 55.6 52 51
775 776 777 778 779 29
Pd (ml/m2/day) 0 40 64 88 112 128 152 160 172 184 188 184 176 164 144 134 112 92
780
Table. 6
781
Hourly variation of measured values for SSSS-CIF with BW insulation (2017/06/02) Sl.No.
I (W/m2)
Tamb (°C)
V (m/s)
Tw (°C)
TCIF (°C)
Tair (°C)
Tic (°C)
9:00 9:30 10:00 10:30 11:00 11:30 12:00 12:30 13:00 13:30 14:00 14:30 15:00 15:30 16:00 16:30 17:00 17:30
580 650 715 754 810 844 857 855 842 806 746 672 590 494 395 308 185 135
26 26.6 34.5 35.4 36.2 36.1 36.3 36 36 36 36.4 35.2 34.5 34.8 36.3 34.5 33.7 33
1.02 2.985 0.82 3.819 3.268 2.926 0.795 2.8 1.05 1.3 2.305 1.869 1.789 1.322 2.159 1.025 3.531 2.309
46.7 48.1 49.2 54.2 59.9 62.7 66 69.3 68.9 70 70.4 71 70 69.1 65.7 63.4 59.7 54.8
47.2 49.7 51.5 56.5 62.1 64.8 67.8 68.9 69.7 70.8 71.9 71.5 69.2 68.1 66 64 60 55.2
49.8 53.1 54.8 58.9 62.4 64.7 68.3 69 68.5 69 70.1 69.3 68.2 68.4 64 60.6 55 52.6
46 47.4 48.6 54.3 58.9 60 62 63.4 64 64.7 65.2 63.5 62.8 61.9 60 56.9 54 53.1
782 783 784 785 786 30
Pd (ml/m2/day) 0 52 100 136 180 212 234 242 250 250 232 216 196 176 156 140 122 96
787
Table. 8
788
Hourly variation of measured values for SSSS with wooden insulation (2017/06/02) Sl.No.
I (W/m2)
Tamb (°C)
V (m/s)
Tw (°C)
Tair (°C)
Tic (°C)
9:00 9:30 10:00 10:30 11:00 11:30 12:00 12:30 13:00 13:30 14:00 14:30 15:00 15:30 16:00 16:30 17:00 17:30
580 650 715 754 810 844 857 855 842 806 746 672 590 494 395 308 185 135
26 26.6 34.5 35.4 36.2 36.1 36.3 36 36 36 36.4 35.2 34.5 34.8 36.3 34.5 33.7 33
1.02 2.985 0.82 3.819 3.268 2.926 0.795 2.8 1.05 1.3 2.305 1.869 1.789 1.322 2.159 1.025 3.531 2.309
43.1 47.6 53 58.4 62.5 65.1 67 68.7 68.1 67.5 66.4 60.9 57.4 54.2 51 47.8 44.6 41.4
45.6 48.8 54 57.8 61.9 63.4 64 66 64.6 64.5 62.6 59.4 56.1 52.4 48 43.6 39.2 34.8
48 51.5 53.9 55.9 56.6 58 59.4 60 59 58.8 57.6 57 56.1 53 50 47 44 41
31
Pd (ml/m2/day) 0 40 60 80 100 120 140 148 160 168 180 180 168 152 140 124 108 84
ACCEPTED MANUSCRIPT Table. 9 Parameters used for simulation S.No. Parameters
Value
Unit
Water 1
Density (ρ)
998.2
kg/m3
2
Specific heat capacity (Cp)
4182
J/kg.K
3
Thermal conductivity (k)
0.6
W/m.K
4
Viscosity
0.001003 Pa.s
5
Molecular weight
18.052
g/mol
Glass 6
Density (ρ)
2500
kg/m3
7
Specific heat capacity (Cp)
750
J/kg.K
8
Thermal conductivity (k)
1.05
W/m.K
CIF absorber 9
Density (ρ)
35
kg/m3
10
Specific heat capacity (Cp)
1200
J/kg.K
11
Thermal conductivity (k)
0.25
W/m.K
700
W/m2
Climatic parameters 12
Solar radiation I(t)
13
Ambient temperature (Tamb) 29
32
°C
ACCEPTED MANUSCRIPT
Table. 10 Water holding capacity of foams and sponge S.No
1 2
Material type Polyurethane foam (high density) Polyurethane foam (low density)
Volume of
Dry
Wet
Weight
the
weight
weight
difference
material
in grams
in grams
in gram
599 cm3
23
412
389
16.91
857 cm3
7
625
618
88.28
Water Held (Wt. diff.÷ Dry Wt.)
3
PVA sponge
222 cm3
31
422
391
12.61
4
CIF
257 cm3
9
257
248
27.55
Table. 11 Cost analysis of experimented solar still designs Components -US$ for 1 m2 still Galvanized iron Top cover Black paint Fresh water port Labor charge Bubble wrap Wooden and saw dust insulation CIF Absorber Pipes Total L/m2/day $/L water Cost increases Output increases
SSSS Without insulation 15 3 1.56 0.7 12.5 N/A N/A N/A 0.78 33.54 1.924 0.0060 -
33
SSSS with BW
SSSS-CIF with BW
15 3 1.56 0.7 12.5 1.55 N/A N/A 0.78 35.09 2.34 0.0051 5% 22%
15 3 1.56 0.7 12.5 1.55 N/A 19.4 0.78 54.49 2.9 0.0064 62% 37%
SSSS with saw dust insulation 15 3 1.56 0.7 13 0 19.46 N/A 0.78 53.5 2.124 0.0086 60% 10%
804 805
Table. 12
806
Comparison of previous work with different insulation material used in the solar still S.No. 1 2
Author Ganaraj et al. (2017), India Rajaseenivasan et al. (2017), India
Solar still design
Thickness/Insulation Productivity
Year/Month
of
experimentation
Single slope solar still
20 mm/saw dust
2345 ml/day
April-May 2016
Single slope solar still
0.025 m/glass wool
3.19 kg/day
June 2014-April 2015
3
Gupta et al. (2016), India
Single slope solar still
20 mm/glass wool
2940 ml/day
April 2015
4
Sharshir et al (2017), China
Single slope solar still
5 mm/ glass wool
2116 ml/day
Nov-Dec 2015
5
Rabhi et al. (2017), Tunisia
Single slope solar still
Plywood
2.34 l/m2
Jan 2016
6
Jamil and Akhtar (2017), India
Single slope solar still
25 mm/glass wool
2.24 l/m2
March to June, 2015
7
Arunkumar et al. (2016), India
Single slope solar still
Saw dust
2.100 l/day
Jan to Nov 2013
8
Arunkumar et al. (2016), India
Single slope solar still
Saw dust
1.600 l/day
May 2012
9
Present work
Single slope solar still
30 mm/bubble-wrap
2.3 l/m2/day
April to June 2017
10
Present work
Single slope solar still
No insulation
1.9 l/m2/day
April to June 2017
807 808 809
34
ACCEPTED MANUSCRIPT
Fig. 1. Details of CIF absorber
Fig. 2. (a) Photograph of CIF top view, (b) side view, and (c) zoomed view (pores) 35
ACCEPTED MANUSCRIPT
Fig. 3. Photographic view of Pyranometer
36
Fig. 4. [A] SSSS without insulation, [B] SSSS with BW insulation, [C] SSSS-CIF with BW insulation, and [D] Conventional solar still
37
ACCEPTED MANUSCRIPT
Fig. 5. (a) Pictorial view of BW insulation front view, and (b) bottom view
Fig. 6. Pictorial view of experimental setup with temperature indicators
Fig. 7. Snapshot of (a) SSSS-CIF with BW, (b) CIF in the basin and (c) trace of larger condensation water marks under the cover 38
ACCEPTED MANUSCRIPT
Fig. 8. Graphical view of solar radiation and ambient temperature with respect to time
39
ACCEPTED MANUSCRIPT
Fig. 9 (a). Temperature profile of SSSS without insulation, (b) Temperature profile of SSSS with BW insulation, (c) Temperature profile of SSSS-CIF with BW insulation and, (d) Temperature profile of CSS
40
ACCEPTED MANUSCRIPT
Fig. 10. Evaporative heat transfer coefficient
Fig. 11 Mesh view of CIF
41
ACCEPTED MANUSCRIPT
Fig. 12. Temperature distribution of floating absorber in the solar still
42
ACCEPTED MANUSCRIPT
Fig. 13. Productivity with respect to solar still experiments
Fig. 14. Photograph of PVA sponge, polyurethane sponges and CIF
43
ACCEPTED MANUSCRIPT
Fig. 15. Photographic view of water holding capacity (dry and wet) of foams and sponges
44
ACCEPTED MANUSCRIPT
Fig. 16. Economics of previous results as compared with present work
45
ACCEPTED MANUSCRIPT
Highlights The temperature distribution of the floating absorber was investigated with CFD. CFD showed good agreement with experiment. Carbon impregnated foam increased productivity by 35%. Bubble-wrap is found to be an inexpensive insulation material.
ACCEPTED MANUSCRIPT Table. 6 Hourly variation of measured values for SSSS with BW insulation (2017/06/02) I (W/m2) 580 650 715 754 810 844 857 855 842 806 746 672 590 494 395 308 185 135
Sl.No. 9:00 9:30 10:00 10:30 11:00 11:30 12:00 12:30 13:00 13:30 14:00 14:30 15:00 15:30 16:00 16:30 17:00 17:30
Tamb(°C) 26 26.6 34.5 35.4 36.2 36.1 36.3 36 36 36 36.4 35.2 34.5 34.8 36.3 34.5 33.7 33
V (m/s) 1.02 2.985 0.82 3.819 3.268 2.926 0.795 2.8 1.05 1.3 2.305 1.869 1.789 1.322 2.159 1.025 3.531 2.309
Tw (°C) 47.3 48.6 51.9 58.6 61.1 63.5 67.6 68.3 69.2 69.8 70.3 69.5 68.9 66.5 64.1 59.8 51.6 50
Tair (°C) 47.1 48.3 50.3 56.4 59.4 62.1 65 66.4 66.9 67.8 69 68.3 67.8 66.3 63.9 60.2 56.4 55
Tic (°C) 46 47.8 49.3 54.8 56.5 58.5 60.6 62.8 63.3 64.7 65.7 63.9 62.2 60.2 59.9 55.6 52 51
Pd (ml/m2/day) 0 40 64 88 112 128 152 160 172 184 188 184 176 164 144 134 112 92
Table. 7 Hourly variation of measured values for SSSS-CIF with BW insulation (2017/06/02) Sl.No. 9:00 9:30 10:00 10:30 11:00 11:30 12:00 12:30 13:00 13:30 14:00
I (W/m2) 580 650 715 754 810 844 857 855 842 806 746
Tamb (°C) 26 26.6 34.5 35.4 36.2 36.1 36.3 36 36 36 36.4
V (m/s) 1.02 2.985 0.82 3.819 3.268 2.926 0.795 2.8 1.05 1.3 2.305
Tw (°C) 46.7 48.1 49.2 54.2 59.9 62.7 66 69.3 68.9 70 70.4
TCIF (°C) 47.2 49.7 51.5 56.5 62.1 64.8 67.8 68.9 69.7 70.8 71.9
Tair (°C) 49.8 53.1 54.8 58.9 62.4 64.7 68.3 69 68.5 69 70.1
Tic (°C) 46 47.4 48.6 54.3 58.9 60 62 63.4 64 64.7 65.2
Pd (ml/m2/day) 0 52 100 136 180 212 234 242 250 250 232
ACCEPTED MANUSCRIPT 14:30 15:00 15:30 16:00 16:30 17:00 17:30
672 590 494 395 308 185 135
35.2 34.5 34.8 36.3 34.5 33.7 33
1.869 1.789 1.322 2.159 1.025 3.531 2.309
71 70 69.1 65.7 63.4 59.7 54.8
71.5 69.2 68.1 66 64 60 55.2
69.3 68.2 68.4 64 60.6 55 52.6
63.5 62.8 61.9 60 56.9 54 53.1
216 196 176 156 140 122 96