Performance Analysis, and Economic-Feasibility Evaluation of Single-Slope Single-Basin Domestic Solar Still under Different Water-Depths

Abstract

The impact of single-slope solar still with and without flat-plate collector was evaluated experimentally and numerically. Experimental analysis was conducted for four different water depths (3, 6, 9, 12 cm) in on-sunshine hours between 11 AM to 5 PM in Bhopal (23.2599° N, 77.4126° E), India. The thermo efficiency was 51.31% for 3 cm water depth while 24.29% for 12 cm water depth in an active mode of operation. In the case of passive mode, the thermo efficiency was 17.02% for 3 cm water depth and 6.77% for 12 cm water depth. The average exergy efficiency of single-slope solar still is 66.60% for 3 cm depth which is higher than 12 cm depth, i.e., 23.14%. The hourly variation parameters of solar still were also calculated and analyzed. The overall results obtained in the analysis state that solar still performs effectively when coupled with a flat-plate solar collector. According to econometric evaluation, the fabrication expense of a single-slope solar-basin-still is 126.43$ whereas the cost of producing distilled water per day is 1.61$, and the payback period of a single-slope solar-basin-still with FPC is 17.53 months. In a nutshell, the single-slope solar-basin-still design is commercially viable, functional, and technically sustainable, minimizing manufacturing costs in comparison with a traditional solar still, and past findings. The proposed solar still produced remarkable results in all experimental trials.

1. Introduction

An adult human body comprises 60% water. This fact indicates the importance of water in our day-to-day life. History has also shown us that important civilizations that grew and flourished were on the banks of rivers where water was in abundance. Additionally, it is well known that water is a prerequisite for life. Nature has gifted water in abundance to us. As we know, out of the Earth’s total surface area, 71% is covered with water, out of which only 2.5% of this is fresh water that can be used by us.

Moreover, the majority of this freshwater is stored in glaciers, which means that the availability of clean water is scarce. There is a severe scarcity of potable drinking water in numerous regions/countries due to the rapid increase in the population. In rural areas, the infrastructure for drinking water is underdeveloped and hence, is unable to meet the requirements of the people [1]. For domestic use, drinking purposes, and industrial and agricultural needs, saline water is not suitable for consumption. Solar energy is feasible and economical for all solar-based appliances [2] Solar desalination is the process of utilizing solar energy and collecting water of low salt concentrate from seawater or saline water. Solar-still systems distill water and then evaporate it using solar energy. Durkaieswaran and Murugavel [3] The evaporated water is collected and purified in condensation traps, which can be utilized for drinking and other purposes. Solar distillation is both economical and pollution free as compared to the other existing desalination methods. Fathy et al. [4] In the case of the conventional methods of desalination, which are energy-intensive, higher productivity is obtained. Lower productivity was obtained for solar stills through the existing desalination methods, and extensive research was carried out to improve the system by installing condensers, basins, reflectors, etc. Single-slope single-basin solar stills are easy to construct and operate [2] The working principle of a solar still is based on evaporation and condensation. The evaporated water produces vapor in the basin, which is then allowed to condensate on a tilted glass cover. This method is environmentally friendly because the prime source of energy is from the Sun. The solar distillation process mainly consists of two modes, i.e., passive and active. In the passive solar still, the system works without a Flat-Plate Collector (FPC), while in active solar still, the system is coupled with FPC. Kumar et al. [5] examined the workings of an evacuated tube solar still and found that the thermo efficiency can be enhanced by minimizing heat losses. Eltawil et al. [6] investigated the productivity of a modified solar still coupled with FPC sprayers, tubes, etc., and found that the productivity was increased by 56% to 82% with the circulation of hot water in active and passive sprayers. Sheeba et al. [7] revealed that both the productivity and efficiency of a solar still increased when operated with saline water in a solar still equipped with FPC. Senthil et al. [8] used a modified solar still attached to a biomass water heater to enhance the evaporation rate and water temperature. The result shows that during sunlight and off-sunshine hours, the yield output increases using biomass heaters. Prakash et al. [9] functioned on a double-slope active solar still equipped with a parabolic-type trough collector and found an increment in the efficiency of about 28.1%. Deshmukh et al. [10] operated on a sensible heat-storage-based single-basin solar still and found an increase in water storage and mass. The result revealed that the productivity increased overnight and decreased with water storage and mass in daylight. Yousef et al. [11] worked on the exergy and energy performance of modified solar still with heat-storage materials, i.e., phase change materials (PCM), and explained that the average efficiency using pin fin PCM is 37.5% as compared to traditional solar stills. Panchal et al. [12]; Panchal and Sathyamurthy [13] studied a double-basin solar still with solid fin equipped with evacuated tubes and found that the distillate output is enhanced by about 25% when solid fins are attached. Rabhi et al. [14] showed a performance study in a single-slope single-basin solar still and found an increase of 32.18% in water production in solar still when coupled with airflow and an external condenser. Dashtban and Tabrizi [15] experimentally found that the total freshwater yield improved from 5.1 kg/m² day for conventional stills to 6.7 kg/m² day for modified still customized using PCM. Ansari et al. [16] in Errachidia city analytically found that the selection of PCM material depends on saline water’s highest value of temperature. Kumar et al. [17] conducted experiments on a hemispherical solar still with a solar concentrator with and without PCM and concluded an increase of 26% in yield for the still equipped with PCM compared to the still without PCM in his work. El-Sebaii et al. [18] analytically concluded using single-slope stills with and without PCM, that as a quantity of PCM is increased, not only nighttime productivity but daily productivity also increases. In contrast the productivity in the daytime decreases. Moreover, the authors also concluded that the freshwater yield increases when the basin is filled at shallow depths of brackish water. Kabeel et al. [19] used a customized solar still that incorporated a solar heater with a PCM storage unit and, through experiments, found a noticeable increase in the freshwater yield from 4.5 L/m² day to 9.36 L/m² day. Haddad et al. [20] employed vertical rotating-wick (VRW) to enhance the performance of the solar still basin. The result shows that the average thermo efficiency with VRW is 65%, and without VRW, it is 46%. García-Chávez et al. [21] performed computational fluid dynamics (CFD) analysis to conduct a thermal study on a solar distiller and observed that the solar still performance is affected by the climatic conditions, wind speed, and yield. The efficiency of the still is increased in accordance with solar radiation. Numerous studies have been conducted to improve solar still production throughout the day and at night. The literature survey made it evident that many researchers had made an attempt to raise the temperature of the water in the basin and enhance the efficiency of solar still.

Table 1. Uniqueness of the current investigation as against existing literature.

Authors	Major Findings	Uniqueness of the Current Investigation
Boopalan et al. [22]	Three-stepped solar stills were used, one without a phase-change substance, one with paraffin wax as a phase-change material, and one with Ca(NO)3 as a phase-change material. By storing solar energy in the form of latent heat, which is released throughout the night to enable solar still distillation, phase change materials are integrated into solar stills to boost the productivity of clean drinking water. When compared to solar stills with paraffin as the phase change material, those with Ca(NO)3 as the phase change material produced 8.17% more clean drinking water.	The impact of single-slope solar stills with and without a flat-plate collector was evaluated experimentally and numerically in the geographical location of Bhopal (23.2599° N, 77.4126° E), India. Experimental analysis was calculated for four different water depths (3, 6, 9, and 12 cm) in on-sunshine hours between 11 AM and 5 PM. The overall results obtained in the analysis state that solar still performs effectively when coupled with a flat-plate solar collector.
Pathak et al. [23]	The efficiency and productivity of solar stills are greatly enhanced by the use of phase change and nanomaterials, making them ideal for industrial applications. The system that includes nanomaterials has a higher heat transfer rate and is more thermally active.
Thakur et al. [24]	Reduced graphene oxide (RGO)-coated absorber plates in sun stills and RGO-coated absorber plates combined with activated carbon pellets as a sensible thermal energy storage medium were used by the authors to increase the performance of single-basin solar stills. The use of activated carbon pellets and absorber plates covered with RGO increased the water yield by 58.15% and the full-day average energy efficiency by 64.44%, according to the results, respectively.
Panchal et al. [25]	The single-basin passive solar still with vacuum tubes was found to be a more productive attachment when compared to solar ponds, parabolic collectors, flat-plate collectors, and flat-plate collectors. The energy payback time of a single-basin passive solar still is 176 days, and the yearly cost of drinkable water is 0.723 INR.

provides the uniqueness of the current investigation as against the existing literature.

The main objective of the present experimentation is to perform a thermal analysis of the proposed setup. Secondly, economic analysis and exergy analysis were conducted to undertake the overall analysis of the system. Therefore, an attempt has been made to analyze the performance of both passive and active types of domestic solar stills. Four diverse water depths with intervals of 3 cm (3, 6, 9, and 12) were selected for the proposed study. The thermo efficiency of the proposed solar still is computed, and the solar still parameters are compared.

2. Methodology

2.1. Experimental Setup

The experimentations were conducted in hot and dry climatic conditions during the sunny period from 11 a.m.–5 p.m. (IST) from 28 April 2022 to 1 May 2022. The proposed setup was titled at the latitude angle of Bhopal, India, i.e., 23.2599° N, 77.4126° E. The inner walls of the solar still basin were 4 mm thick and were of fiber-reinforced plastic (FRP). The still basin bottom surface area has a dimension of (50.80)² cm², and muddy black paint was applied to enhance the absorptivity, i.e., ‘ε’ = 0.88. The refractive index determines the differences between the angle of incidence and the transmission of light, with a higher index implying greater differences. The glasses used in solar stills have a refractive index of 1.5, which means that reflection losses at the surface result in approximately a 4% decrease in light intensity. In a solar still basin, hot water flows naturally to improve the temperature difference among the water surface, and glass has an absorptivity of 0.04. The area of the FPC is 5,960,000 cm² and is tilted at a latitude angle (23.2599° N, 77.4126° E). The FPC and solar still are coupled together to circulate water in a passive mode. Figure 1 shows the schematic view, and Figure 2 depicts the experimental setup of the solar still (single slope) connected with FPC.

Table 2. (a). Specifications of proposed solar-still design. (b). Specs of proposed flat-plate solar collector.

(a)
S. No.	Solar Still Basin Dimensions		Glass Cover Dimensions
1.	Area—50.80 cm × 50.80 cm		Thickness—5 mm
2.	Basin material—FRP of 4 mm thickness		Inclination— (23.2599° N, 77.4126° E)
3.	Lower height of basin—20.32 cm Higher height of basin—48.26 cm		Breadth—50.8 cm
4.	Length—50.792 cm Width—50.792 cm		Length—58.42 cm
(b)
S. No.	Heating-Pipes	Box	Absorber Plate
1.	${(\alpha \tau )}_c$= 0.8	Area ofglasscoverBox 55.88 × 106.68 cm2	Sheet thickness = 5 mm
2.	Length = 91.44 cm, Total no of pipes = 5, Diameter 1.905 cm. Length = 50.8 cm, Total no of pipes = 2, Diameter 2.54 cm.	Glass Cover Thickness of box = 5 mm	Material of absorber plate = M.S Sheet
3.	Material of heating pipes: M.S pipes	Material: FRP Sheet Dimensions: 106.68 × 55.88 × 12.7 cm3	Length of absorber plate = 106.68 cm; Thickness of absorber plate = 5 mm Breadth = 55.88 cm
4.			Distance of tube (Centre to Centre)—7.62 cm

a depicts the specifications of the proposed solar still design. Table 2b shows the specifications of FPC. The rubber gasket is used to fix the condensing cover to the top of the vertical walls.

2.2. Equipment

The solar still performance was evaluated on the basis of hourly output, hourly variations in solar intensity, water temperature, glass temperature, and ambient temperature for different water depths. To measure the water vapor and glass temperatures, digital temperature and thermocouples (calibrated) were used. A solar power meter with a least count of 1 W/m² was used to measure the solar intensity. A digital anemometer equipped with a humidity test meter and temperature sensor detects the temperature outside and within the proposed solar still, as well as the mass flow rate of air and relative humidity.

Table 3. Uses, accuracies, and ranges of the measuring devices used for experimentation.

S. No.	Instrument	Accuracy	Range	Uses
1	Thermometer	±1 °C	0–100 °C	Measuring Temperature
2	Thermocouple	±1 °C	0–100 °C	Measuring Temperature
3	Pyranometer	0–1000 W/m2	±1 W/m2	Measuring Solar Radiation
4	Anemometer	0–25 m/s	±0.1 m/s	Measuring Wind velocity
5	Measuring beaker	0–500 mL	±2 mL	Measuring Distillate water

provides details on the full measuring instrument’s specifications.

2.3. Experimental Procedure and Observations

The experiment was conducted in sunny hours between 11:00 am to 05:00 pm in Bhopal. The latitude location of the experimental testing was 23°, and the experiment was performed in hourly variation. For mathematical calculations, the total and diffuse radiation on the collector and glass, inner and outer glass temperature, vapor, and water temperature, ambient temperature, distillate output, wind velocity, and relative humidity are the hourly variation parameters at different water depths. These parameters were observed, considering one water depth each day. The parametric values measured are used in the thermal analysis of active and passive solar stills.

2.4. Experimental Uncertainty

Many variables influenced error and uncertainty analysis, including environmental conditions, experiment instruments, test preparation, observation, reading, and calibration. In the current experiment, various parameters have been examined, necessitating the calculation of parameters including temperature, wind velocity at the dryer’s outlet and inlet, and sun intensity. The most effective instrument for planning and carrying out an experiment is uncertainty. The uncertainty analysis can be evaluated as per Equation (1): [26,27]

$$w_R=\sqrt{\left[{\left(\frac{\partial R}{\partial x_1}{w}_1\right)}^2+{\left(\frac{\partial R}{\partial x_2}{w}_2\right)}^2+{\left(\frac{\partial R}{\partial x_3}{w}_3\right)}^2+\dots +{\left(\frac{\partial R}{\partial x_n}{w}_n\right)}^2\right]}$$

(1)

where, $x_1,x_2,x_3,\dots ,x_n$ and $w_1,w_2,w_3,\dots ,w_n$ are independent parameter while, R and $w_R$ are the result of the given function.

The total uncertainty for the measurement of the temperature will be calculated as Equation (2):

$$w_T=\sqrt{\left[{\left(w_{th}\right)}^2+{\left(w_r\right)}^2\right]}$$

(2)

$$w_T=\sqrt{\left[{\left(0.1\right)}^2+{\left(0.1\right)}^2\right]}=\pm 0.1414$$

The total uncertainty for the measurement of wind speed will be calculated as Equation (3):

$$w_w=\sqrt{\left[{\left(w_{an}\right)}^2+{\left(w_r\right)}^2\right]}$$

(3)

$$w_w=\sqrt{\left[{\left(0.01\right)}^2+{\left(0.01\right)}^2\right]}=\pm 0.01414$$

The total uncertainty for the evaluation of solar radiation will be calculated as Equation (4):

$$w_{\mathrm{i}}=\sqrt{\left[{\left(w_{pyrometer}\right)}^2+{\left(w_r\right)}^2\right]}$$

(4)

$$w_{\mathrm{i}}=\sqrt{\left[{\left(0.1\right)}^2+{\left(0.1\right)}^2\right]}=\pm 0.1414$$

The total uncertainty of the experiment will be calculated as Equation (5):

$$w_{\mathrm{ex}}=\sqrt{\left[{\left(w_T\right)}^2+{\left(w_w\right)}^2+{\left(w_{\mathrm{i}}\right)}^2\right]}$$

(5)

$$w_{\mathrm{ex}}=\sqrt{\left[{\left(0.1414\right)}^2+{\left(0.01414\right)}^2+{\left(0.1414\right)}^2\right]}=\pm 0.2004\%$$

It has been observed that all uncertainties were in the acceptable range. Table 3 shows the uses and accuracy of the measuring devices used for experimentation.

3. Performance Analysis

In this analysis, the efficiency of FPC and active solar still needs to be calculated. The inlet water temperature was heated by the collector, and the temperature of the water was increased after achieving a useful amount of energy [28]. The useful energy gained by FPC can be calculated by using Equation (6).

$${\mathrm{Q}}_{\mathrm{u}}=\stackrel{.}{\mathrm{m}}{.\mathrm{C}}_{\mathrm{p}}{.(\mathrm{T}}_{\mathrm{o}}{-\mathrm{T}}_{\mathrm{i}})$$

(6)

The thermo efficiency of FPC is described as the proportion of usable energy to the energy incident on the glazing area (aperture) and was calculated with Equations (7) and (8), [29].

$${\mathsf{\eta }}_{\mathrm{i}}=\frac{{\mathrm{Q}}_{\mathrm{u}}}{\mathrm{A}.\mathrm{I}\left(\mathrm{t}\right)}$$

(7)

$${\mathsf{\eta }}_{\mathrm{i}}=\frac{\stackrel{.}{\mathrm{m}}{.\mathrm{C}}_{\mathrm{p}}{.(\mathrm{T}}_{\mathrm{o}}{-\mathrm{T}}_{\mathrm{i}})}{\mathrm{A}.\mathrm{I}\left(\mathrm{t}\right)}$$

(8)

3.1. The Efficiency of Proposed Solar-Still System Coupled with Flat-Plate Collector

The efficiency of the proposed solar still coupled with FPC is expressed as the proportion between the total amount of energy utilized to acquire distilled water within a specific duration and the amount of energy supplied to the solar still during the same time duration. The efficiency equation is given in Equations (9) and (10).

$$\mathrm{Efficiency}=\frac{\mathrm{Yield} \mathrm{of} 24 \mathrm{hours}\times \mathrm{Latent} \mathrm{heat} \mathrm{of} \mathrm{Evaporisation}}{\mathrm{Incident} \mathrm{energy} \mathrm{on} \mathrm{collector}+\mathrm{Incident} \mathrm{energy} \mathrm{on} \mathrm{solar} \mathrm{still}}\times 100\%$$

(9)

$$\mathrm{Efficiency}=\frac{{\displaystyle {\displaystyle \sum {\stackrel{.}{m}}_{ew}}}\times {\mathrm{L}}_{\mathrm{v}}}{{\displaystyle \sum {\mathrm{I}}_{\mathrm{g}}\times {\mathrm{A}}_{\mathrm{collector}}\times 6\times 3600}+{\displaystyle \sum {\mathrm{I}}_{\mathrm{g}}\times {\mathrm{A}}_{\mathrm{glass}}\times 6\times 3600} }\times 100\%$$

(10)

In the case of the passive solar still, the incident energy on the collector was not considered because of the absence of FPC. Only the effect of the glass-cover solar still will be the incidence of the solar energy input [30].

3.2. Economic & Exergy Analysis

The primary goal of any solar-still system is to reduce the cost of distillate water production per liter (CPL). The researched examples are economically examined, and the economic analysis techniques can be reduced as follows:

According to Equation (11), a solar distillation unit’s first annual cost (FAC) is as follows:

$$FAC=P\times CRF$$

(11)

where P and CRF stand for the solar still’s capital cost and capital recovery factor, respectively.

The CRF is calculated as follows:

$$CRF=\frac{i{(1+i)}^n}{{(1+i)}^n-1}$$

(12)

where n represents the lifetime years of the solar still, which are assumed to be ten years, and i is the annual rate of interest.

According to Equation (13), the solar distillation unit’s annual salvage value (ASV) is as follows:

$$ASV=S\times SSF$$

(13)

where SSF and S stand for a system sinking fund factor (SFF) and the solar still salvage value, respectively.

S is revealed in Equation (14):

$$S=P\times 0.2$$

(14)

SSF can be evaluated as:

$$SSF=\frac{i}{{(1+i)}^n-1}$$

(15)

The AMC is supposedly 15% of the initial annual cost:

$$AMC=FAC\times 0.15$$

(16)

Equation (17) provides the solar distillation unit’s total annual cost as follows:

$$TAC=AMC+FAC-ASV$$

(17)

Lastly, the freshwater yield’s cost per liter (CPL) is calculated using Equation (18)

$$CPL=\frac{TAC}{P_n}$$

(18)

where P_n is the average annual production of distilled water.

The exergy analysis function represents an indicator of the energy’s ability to conduct work and is derived from the second law of thermodynamics. Exergy is defined as the maximum amount of work that a system is capable of producing when it approaches thermodynamic equilibrium in a particular environment. The general equation for the exergy balance is given below:

$${{\displaystyle \sum \stackrel{.}{E}}}_{x,i}={{\displaystyle \sum \stackrel{.}{E}}}_{x,o}={{\displaystyle \sum \stackrel{.}{E}}}_{x,d}$$

(19)

The exergy input of the proposed system is evaluated as per Equation (20):

$${{\displaystyle \sum \stackrel{.}{E}}}_{x,i}={{\displaystyle \sum \stackrel{.}{E}}}_{x,s}=A_b{I}_t\left[1-\frac{4}{3}\left(\frac{T_{ambt}+273}{T_S}\right)+\frac{1}{3}{\left(\frac{T_{ambt}+273}{T_S}\right)}^4\right]$$

(20)

While the exergy output of the proposed system is evaluated as per Equation (21):

$${\stackrel{.}{E}}_{x,o}={\stackrel{.}{E}}_{x,ev}=\frac{m_{ew}{\lambda }_{lt}}{3600}\left[1-\left(\frac{T_{ambt}+273}{T_{wr}+273}\right)\right]$$

(21)

The exergy efficiency is calculated as the difference between the input and output exergy, and it is written as follows:

$${\eta }_{ex}=\frac{{\stackrel{.}{E}}_{x,ev}}{{\stackrel{.}{E}}_{x,in}}$$

(22)

4. Result and Discussion

4.1. Experimentation Data Analysis

The vapor temperature, quasi-steady static condition, and vapor leakage were analyzed in the present experimentation. The observations are listed between

Table 4. (a). Experimental observations of single-slope solar still without FPC at 3 cm water depth. (b). Experimental observations of single-slope solar still with FPC at 3 cm water depth.

(a)
S. No.	Time	γa	Ta	Id(Inc)	vg	Tw	Ig(Inc)	Tv	Tgi1	Tgo1	mew1
	(h)	(%)	(°C)	(W/m2)	(m/s)	(°C)	(W/m2)	(°C)	(°C)	(°C)	(mL/h)
1	11:00	35.6	36.8	164	0.16	18	998	14	15	15	0
2	12:00	35.1	36.8	171	0.14	15	1018	11	13	13	46
3	13:00	32.2	37.5	158	0.22	16	1000	12	15	18	76
4	14:00	30.4	37.9	900	0.12	15	912	11	15	16	125
5	15:00	26.1	38.3	708	0.08	26	637	16	28	30	194
6	16:00	24.6	39.4	552	0.24	25	570	15	27	29	220
7	17:00	24.6	35.6	303	0.16	21	321	14	22	24	260
(b)
S. No.	Time	γa	Ta	Id2(Inc)	vg	Tw	Ig2(Inc)	Tv	Tgi2	Tgo2	Mew2
	(h)	(%)	(°C)	(W/m2)	(m/s)	(°C)	(W/m2)	(°C)	(°C)	(°C)	(mL/h)
1	11:00	23.4	38	140	0.04	28	1017	24	18	18	0
2	12:00	21.9	38.6	135	0.07	27	1023	25	18	17	55
3	13:00	20.6	39.6	106	0.36	19	1037	11	14	15	99
4	14:00	20.9	39.6	910	0.08	20	650	14	10	11	160
5	15:00	19.9	39.7	743	0.06	23	663	13	17	18	485
6	16:00	18.3	40.7	592	0.16	22	584	12	21	22	500
7	17:00	17.8	40.5	116	0.18	21	318	17	25	27	525

,

Table 5. (a). Experimental observations of single-slope solar still without FPC at 6 cm water depth. (b). Experimental observations of single-slope solar still with FPC at 6 cm water depth.

(a)
S. No.	Time	γa	Ta	Id(Inc)	vg	Tw	Ig(Inc)	Tv		Tgi1	Tgo1	Mew1
	(h)	(%)	(°C)	(W/m2)	(m/s)	(°C)	(W/m2)	(°C)		(°C)	(°C)	(mL/h)
1	11:00	38.1	36.2	154	0.08	24	410	22		20	20	0
2	12:00	35.7	37.27	138	0.01	27	1015	23		18	17	21
3	13:00	31.1	38.22	144	0.04	18	1048	18		16	18	61
4	14:00	26.8	38.22	145	0.03	17	934	14		15	18	104
5	15:00	27.7	37.88	102.3	0.11	18	140.2	19		20	22	120
6	16:00	27.7	37.61	32	0.01	24	58	22		23	23	180
7	17:00	27.7	37.33	15	0.02	27	18	21		22	23	210
(b)
S. No.	Time	γa	Ta	Id2(Inc)	vg	Tw	Ig2(Inc)	Tw	Tv	Tgi2	Tgo2	Mew2
	(h)	(%)	(°C)	(W/m2)	(m/s)	(°C)	(W/m2)	(°C)	(°C)	(°C)	(°C)	(mL/h)
1	11:00	31.2	37.1	107	0.26	25	955	25	21	17	18	0
2	12:00	27.9	37.9	94	0.25	23	448	23	19	18	18	16
3	13:00	24	38.7	114	0.11	22	978	22	9	15	15	49
4	14:00	20.3	40.7	903	0.24	20	898	20	3	14	15	89
5	15:00	20.7	39.7	108	0.12	15	733	15	5	20	20	154
6	16:00	22.2	39.5	116	0.16	18	574	18	16	24	25	182
7	17:00	21.4	39.4	74	0.12	17	308	17	16	27	27	240

,

Table 6. (a). Experimental observations of single-slope solar still without FPC at 9 cm water depth. (b). Experimental observations of single-slope solar still with FPC at 9 cm water depth.

(a)
S.No	Time	γa	Ta	Id(Inc)	vg	Tw	Ig(Inc)	Tv	Tgi1	Tgo1	Mew1
	(h)	(%)	(°C)	(W/m2)	(m/s)	(°C)	(W/m2)	(°C)	(°C)	(°C)	(mL/h)
1	11:00	32.8	34.27	102	0.18	28	233	22	23	24	0
2	12:00	30	35.11	200	0.01	27	435	22	22	23	3
3	13:00	29.3	35.5	140	0.28	24	255	13	23	25	14
4	14:00	27.9	35.88	237	0.06	22	411	5	23	25	40
5	15:00	30.2	35.7	604	0.08	22	702	2	20	20	74
6	16:00	33.1	36.61	151	0.12	21	212	19	23	25	112
7	17:00	35.4	36.72	92	0.14	22	290	12	26	28	140
(b)
S. No.	Time	γa	Ta	Id2(Inc)	vg	Tw	Ig2(Inc)	Tv	Tgi2	Tgo2	Mew2
	(h)	(%)	(°C)	(W/m2)	(m/s)	(°C)	(W/m2)	(°C)	(°C)	(°C)	(mL/h)
1	11:00	42.3	35.4	147	0.11	25	956	24	15	16	0
2	12:00	39.2	36.2	178	0.13	26	1050	23	17	16	8
3	13:00	31	37.5	144	0.042	25	1047	23	26	27	35
4	14:00	27.3	38.5	98	0.02	25	930	24	15	16	48
5	15:00	25.2	39	730	0.14	26	754	17	18	18	160
6	16:00	23.9	38.7	550	0.09	22	552	23	24	19	187
7	17:00	21.9	38.8	95	0.15	25	332	22	24	23	224

and

Table 7. (a). Experimental observations of single-slope solar still without FPC at 12 cm water depth. (b). Experimental observations of single-slope solar still with FPC at 12 cm water depth.

(a)
S. No.	Time	γa	Ta	Id(Inc)	vg	Tw	Ig(Inc)	Tv	Tgi1	Tgo1	Mew1
	(h)	(%)	(°C)	(W/m2)	(m/s)	(°C)	(W/m2)	(°C)	(°C)	(°C)	(mL/h)
1	11:00	31.9	37.5	134	0.22	30	970	23	16	16	0
2	12:00	31.9	36.5	112	0.08	28	1028	22	15	16	10
3	13:00	27.5	37.3	142	0.14	28	987	12	15	16	16
4	14:00	26.8	37.8	866	0.26	19	815	15	19	26	25
5	15:00	34.4	36.3	856	0.14	20	835	19	18	18	33
6	16:00	31.5	36.9	165	0.26	26	370	8	20	20	43
7	17:00	32.4	35.9	62	0.27	27	90	20	22	22	224
(b)
S. No.	Time	γa	Ta	Id2(Inc)	vg	Tw	Ig2(Inc)	Tv	Tgi2	Tgo2	Mew2
	(h)	(%)	(°C)	(W/m2)	(m/s)	(°C)	(W/m2)	(°C)	(°C)	(°C)	(mL/h)
1	11:00	37.7	36.5	188	0.18	22	1002	20	19	18	0
2	12:00	35.1	36.4	109	0.27	22	229	22	20	19	8
3	13:00	32.8	37.7	204	0.15	19	1100	18	19	18	15
4	14:00	53.5	31.4	19.6	0.1	15	25	19	22	21	40
5	15:00	48.3	32.3	55	0.06	16	103	16	22	21	57
6	16:00	44	32.7	435	0.12	18	419	19	21	20	84
7	17:00	36.8	35.2	92	0.12	16	475	19	25	25	105

at four different water depths (3, 6, 9, and 12 cm) of active and passive types of single-slope solar still from 11:00 to 17:00 h (6 h per day).

Parameters such as the ambient temperature and sun radiation can be used to perform the heat transfer analysis. The temperature within the solar still varies as a result of these factors. For the desalination process, relative humidity is crucial. The variance in the temperature is determined by the variation in the relative humidity. The moisture content of the air increases as relative humidity increases, resulting in a drop in air temperature.

It is very well known that the volume of yield output depends on the evaporative surface and the condensing surface. As the temperature difference between them enhances, the yield output of the solar still also increases. All the parametric effects on yield, convective heat-transfer coefficients, evaporative heat-transfer coefficients, and thermo efficiency are discussed in this section.

In Table 4, Table 5, Table 6 and Table 7, the ambient temperature and relative humidity variations are shown with respect to the global and the diffused radiations at 3, 6, 9, and 12 cm water depths. There is an effect on the ambient temperature due to a decrease in global and diffuse radiations since the observations are made between 11:00 and 17:00 h. It was observed that the relative humidity is inversely proportional to ambient temperature.

The variation in the temperature of the water, both, inside the glass as well as outside, with respect to diffuse global radiations with time were also shown in Table 4, Table 5, Table 6 and Table 7. The inner glass temperature is higher at a lower depth of water at 15:00 h. The temperature of the water is maximum when the Ig is at the peak.

It is inferred from the table that the yield of the solar still is maximum at the peak point of solar radiation. However, in the case of 12 cm depth, the yield is maximum, and it is concluded that the storage effect of heat results in an increment of yield output.

The variations in yield and wind velocity with respect to time are indicated at four different water depths (3, 6, 9, and 12 cm). From the table, it can be inferred that with the increase in wind velocity, the convective heat transfer coefficient also increases. If the temperature difference increases, then the yield also increases. Whenever there is an increase in the wind velocity, the yield will be reduced due to heat loss on the surface of glass and this can be clearly observed in the case of 9 cm water depth. Table 3, Table 4, Table 5 and Table 6 also show the variation in the yield per hour of a single-slope solar still with respect to water temperatures, inner glass, and time. It is concluded from the chart that yield is maximum in case of 12 cm water depth because of the difference in water temperatures. When the water-temp. is maximum, the distillate output rate enhances. As the difference in temperature increases, evaporation increases, and hence, the yield output also increases.

4.2. Exergy Analysis

Exergy is found to be higher due to solar irradiation. However, the same is not true for the exergy efficiency of a solar collector. Moreover, the exergy efficiency improved with increases in the temperature of the solar collector. The highest increase in exergy efficiency was achieved at the highest temperature. Therefore, considering the economic aspect and increased costs, heat storage-based materials were considered for the system to provide a constant temperature.

Table 8. Exergy analysis of proposed solar still at different depth.

Time	Depth (3 cm)			Depth (6 cm)			Depth (9 cm)			Depth (12 cm)
	Exi	Exo	neff	Exi	Exo	neff	Exi	Exo	neff	Exi	Exo	neff
11	1170.	0.35	0.029	1086.	0.4	0.0392	1004.7	0.20	0.0207	1123.9	0.20	0.01
12	1221	1.24	0.101	1132	1.4	0.1264	1050.7	0.35	0.0335	1033.4	0.12	0.01
13	1258	3.30	0.262	1114	1.7	0.1581	1142.2	1.13	0.0997	1097.0	1.70	0.15
14	1002.	4.79	0.478	946.44	3.5	0.36980	1022.63	1.81	0.17767	1006.56	2.52	0.25
15	801.7	7.50	0.935	828.3	4.9	0.5992	741.37	3.46	0.4669	810.99	2.57	0.31
16	708.6	8.13	1.148	726.1	6.2	0.8603	652.16	4.38	0.6720	641.66	2.44	0.38
17	606.2	10.3	1.709	558.9	6.5	1.1794	539.84	5.2	0.9632	530.19	2.75	0.51

depicts the daily exergy output and exergy efficiency. Equation (15) provides the daily exergies according to varying depths, as shown in Table 7. It has been observed that the highest ᶯ is obtained for the proposed system at the 3 cm basin depth and lowest at 12 water depth as the heat obtained in the depth of 3 cm is higher due to the presence of a lower amount of water in comparison to the depth of 12 cm.

4.3. Cost Analysis

The cost of the solar desalination unit is affected by inlet water properties, water quantity, unit, and location site. Its cost is mainly influenced by capital cost, annual interest rate, depreciation value, annual average production in liters, maintenance cost, and expectancy of the system. The fabrication cost and GST for the solar still are not considered [31,32].

Table 9. Cost of solar still.

Components	Amount (INR)
Silicon seal	645.00
Thermocouple wire (K type)	1100.00
Sealant	260.00
Glass cover	369.00
EGT cap	550.00
Thermocol	230.00
GI sheet	1834.00
Fiber reinforced plate	550.00
Collecting tank	276.00
Manufacturing cost	1194.00
Iron stand	734.00
Paint	276.00
Supply tank	184.00
Plywood	645.00
Total cost	8847.00

depicts the component price in Indian currency. It has been observed that the maximum cost was acquired by the GI sheet while the minimum cost was acquired by the Supply tank. The ratio of the total annual cost and annual average production in liters were considered in calculating the unit cost of saline water.

Table 10. Economic parameters for the proposed system.

Details	Value
Total annualized cost	2260.00 INR
Average salvage cost	385.00 INR
Annualized capital cost	2645.00 INR
Annual Maintenance cost	0
Salvage value in future	2260.00 INR
Life span of the proposed system	20
Sinking fund	0.016
Interest rate	10%
Recovery factor (Capital)	0.116
Number of on-sunshine days	285

depicts the various economic factors of all parameters.

The payback period is the minimum time needed to recoup/recuperate the initial outlay or capital investment. The factors considered for calculating the payback period includes fabrication, operating, and maintenance cost. The payback period of the proposed setup is calculated as 1.46 years, while the cost of water produced per liter is analyzed as 1.61 INR.

Table 11. Payback duration of single-slope solar basin still with FPC.

Details	Amount
Fabrication cost	322.95 INR
Payback period (years)	1.46
Annual output (Kg/day)	6.17
Distillate water	20
Cost of water produced per day	1.61 INR

indicates the payback duration of single-slope solar basin still with FPC.

4.4. Validation

The efficiency of the solar still is 51.31% for the water depth of 3 cm with FPC and is lower at 8.87% at 9 cm depth without FPC. As the experimental setup is situated at the latitude angle of 23° N, nocturnal distillation tendency is the factor of the higher water depth [33,34]. However, at the morning time of observation at 11:00 h, the initial temperature is higher at the initial stage at 3 cm and then decreases at 6 cm, 9 cm, and 12 cm depth, respectively. The efficiency has been compared with Farid and Hamad [35] and it was found that the proposed solar still is more efficient in comparison to other investigators, as shown in

Table 12. Comparative Table.

S. No.	System	3 cm Depth	6 cm Depth	9 cm Depth	12 cm Depth
1.	Single-basin solar still [35]	40%	38%	-	-
2.	Proposed System thermal efficiency	51.31%	41%	26.75%	24.29%

.

5. Conclusions

In this paper, an investigational study of a modified solar still with FPC and its effects was carried out. From the different parameters, it is observed that the highest yield of the experiment is 0.238 kg/h. The hourly variations in the distillate output is dependent upon the radiation throughout the day. The experimental location latitude angle of 23° (Bhopal) yields more when the solar still is coupled with FPC. The following conclusions are drawn from the paper:

(i).

Thermal efficiency of solar still coupled with FPC at a water depth of 3 cm is 51.31%, which is the highest.

(ii).

Thermal efficiency of solar still without FPC at a water depth of 9 cm is 17.02%, which is 66.82% lower than 3 cm.

(iii).

The overall thermal efficiency of a solar still coupled with FPC is 42.065%, while for a solar still without FPC, it is 13.955%.

(iv).

The cost of the proposed solar still is 8847INR; hence the payback period of the proposed system is found as 1.46 years, which is comparatively lower than the traditional solar still.

(v).

Relative humidity varies inversely with ambient temperature.

(vi).

The solar still yield is maximum at the peak point of solar radiation.

(vii).

Whenever there is an increase in the wind velocity, the yield will be reduced due to heat loss on the surface of glass and this can be clearly observed in the case of 9 cm water depth.

(viii).

Highest ᶯ is obtained for the proposed system at the 3 cm basin depth and lowest at 12 water depth.

(ix).

The proposed modified solar still can be used anywhere in the world with a small modification.