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International Journal of Photoenergy
Volume 2018 (2018), Article ID 7978901, 9 pages
https://doi.org/10.1155/2018/7978901
Research Article

Photovoltaic Energy-Assisted Electrocoagulation of a Synthetic Textile Effluent

1Unidad Académica Profesional-Acolman, Universidad Autónoma del Estado de México, Camino de Caleros No. 11, Ejidos de Santa Catarina, Acolman, MEX, Mexico
2Instituto Nacional de Electricidad y Energías Limpias, Av. Reforma 113, Col. Palmira, 62490 Cuernavaca, MOR, Mexico

Correspondence should be addressed to Thelma Beatriz Pavón-Silva; moc.liamg@novap.ht

Received 13 July 2017; Revised 9 October 2017; Accepted 7 November 2017; Published 7 March 2018

Academic Editor: Carlos A. Martínez-Huitle

Copyright © 2018 Thelma Beatriz Pavón-Silva et al. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

Abstract

The feasibility of using photovoltaic modules to power a continuous 14 L electrochemical reactor applied to remove an azo dye with an efficiency of 70% is reported. The photovoltaic modules were directly connected, and the system efficiency was observed properly maintained when currents were applied in the range of 2.5 to 7.9 A. This value depends on solar radiation. Likewise, it was found that the efficiency depends mainly on the current density and the flow rate prevailing in the reactor.

1. Introduction

The problem of industrial wastewater is a topic that deserves special attention, particularly for industries that use dyes and thus generate large volumes of polluted wastewater. Due to their high molecular weights, complex structures, and especially high solubility in water, dyes persist once discharged into a natural environment, for example, textile [1, 2], pharmaceutical [3], cosmetics and food industry [4], and industrial wastewater [5]. Specifically for the textile industry, the chemical structure of these compounds is complex, generally of the type azo [68]. This group consists of colored substances with a complex chemical structure (many functional groups) and a high molecular weight. Thus, their removal from industrial effluents is also a subject of major importance from the environmental point of view. The removal of dissolved organic matter by coagulation is widely reported in literature [9], where the primary mechanism consists of two methods [10]. The first is binding the metal species to anionic sites of the organic molecules, thereby neutralizing their charge and resulting in reduced solubility. The second is the absorption of organic substances on amorphous metal hydroxide precipitates.

Chemical coagulation/flocculation is the most widely used technique for textile wastewater treatment; they have some disadvantages, such as needing pH adjustment before and after treatment, producing large amounts of sludge, and adding undesirable inorganic chemicals like aluminum, iron, sulfate, and chloride to the environment [11].

The results for the optimization of the effect of the coagulation–flocculation showed the rate of dye removal increased from 11.25% to 13.20 for the methylene blue and from 27.5% to 29.25 for the indigo carmine when the concentration of coagulant and flocculant were varied from 40 to 120 mg·L−1. These results confirm the poor applicability of this process for the elimination of such dyes. Assadia et al. [12] show that ferric chloride and alum at optimum concentration were capable of removing dye and COD by 79.63% and 84.83% and 53% and 55%, respectively.

The electrocoagulation process is deemed an economical and environmental choice to minimize the drawbacks of conventional wastewater treatment technologies [13]; it provides a number of benefits, such as low cost, compatibility, and safety [14]. In addition, electrocoagulation has been proven to eliminate complex contaminants in wastewater that require a combination of physicochemical and biological methods [1517]. Its combination with other processes, like ozonation [18], has also been demonstrated to be highly effective for complex matrix wastewater remediation. The application of electrocoagulation, however, has been restricted at some extent by the cost that implies electrical energy usage. Moreover, climate change motivates research and development of new forms of renewable energy [19, 20] such as photovoltaic (PV) power [8], whose advantages include its free use and abundant availability, is a renewable resource, decentralized, with long life span and low maintenance costs, and does not result in contamination.

In this research, a PV system was evaluated in a pilot electrochemical wastewater reactor using a synthetic wastewater model containing azo dye, in this case remazol yellow dye 3GL (RYD), which is mainly used in textile industry [4, 8, 21]. This was first accomplished with batch tests and then with continuous tests in a pilot reactor, both of which are based on previously reported studies [8].

2. Experimental

The experimental setup is shown in Figure 1 and consists of the following: (1) the sun as a renewable energy source; (2) photovoltaic modules to convert sunlight into electricity; (3) an acrylic cylindrical reactor with a 0.15 m diameter and one meter length (14 L of water was treated); (4) direct connection of the sun to the electrochemical reactor, two aluminum electrodes formed by 39 circular blades (0.12 m diameter) with total surface area of 0.44 m2, separated from each other by one centimeter. (5) Registration data and continuous monitoring was performed by a data acquisition system: current, voltage, and solar radiation. (6) The pH, conductivity, and temperature were measured with an electrical conductivity meter.

Figure 1: Scheme of the experimental system: 1, solar energy; 2, photovoltaic module; 3, electrochemical reactor; 4, direct connection of the power supply; 5, parameter control: current, voltage, and solar radiation; 6, pH, conductivity, and temperature control.
2.1. Reagents

The working solution was prepared by dissolving remazol yellow dye (RYD) 3GL (DyStar SA™) in potable water and was used as wastewater model containing azo dye (RYD) as pollutant. Table 1 summarizes its characteristics.

Table 1: Characterization of the remazol yellow dye.

The conductivity was set at 366–380 μS/cm, and this in concordance with Can et al. [22], who stated this parameter to be lower than 500 μS/cm. They investigated the conductivity between 250 and 4000 μS/cm using NaCl as the support electrolyte and noticed that above 500, the remazol red dye removal efficiency decreases. In our case, due to the size of the reactor (14 L pilot reactor), it was decided to work with potable water that already has a conductivity of 302–315 μS/cm, so an electrolyte support was not added. Thus, as reported by Can et al., the decline in the fading efficiency with increasing conductivity can be attributed to a change in ionic strength due to the change in conductivity of the aqueous medium. Ionic strength affects the kinetics and equilibrium of reactions between charged species during electrocoagulation.

2.2. Determination of Remazol Yellow Dye (RYD)

RYD concentration was determined by UV-Vis spectrophotometry in a Perkin Elmer Lambda 2 spectrophotometer. The concentration of the molecule was determined by its absorption at 269.2 nm. The calibration curve was carried out between 0 and 100 mg·L−1 of RYD obtaining the following model: A = 0.0301(C)–0.0003, where A = absorption and C = concentration of RYD. The determination coefficient was r2 = 0.9994. Color determination was conducted in a Hach DR/3000 spectrophotometer.

2.3. Removal Efficiency of RYD

The removal efficiency of RYD was calculated as where C1 is the initial dye concentration and Cf is the final dye concentration, both in mg·L−1; this expression was also used in case of color determination where C1 and Cf are color intensities in Pt/Co units [23].

2.4. Chemical Oxygen Demand

Chemical oxygen demand was determined according to standard techniques, APHA/AWWA/WPCE [24].

The removal efficiency or percentage of COD removal (%RE) was then calculated as follows [25, 26]: where COD0 is the initial chemical oxygen demand and CODf is the final chemical oxygen demand, both in mg·L−1.

2.5. Sampling

The determination of RYD and the removal efficiency of RYD and COD correspond to the samples taken in the upper part of the reactor and later filtered with Whatman paper number 1. The samples were withdrawn from the reactor every 5 min for analysis.

2.6. Applied Current Intensity

The experimental tests were divided into two stages. First, a series of discontinuous tests with current intensities of 4, 6, 8, and 10 A controlled by a power supply during 60 minutes (system DC power supply, Agilent Technologies N5700 series) were carried out and then with current intensities of 2, 3, 4, and 5. The second phase was carried out in a continuous flow, during approximately 6 hours; the current intensity was applied according to the results obtained in the discontinuous tests.

The objective in this stage was to evaluate the intensity of the current that is variable, depending on the following flow rates: 300, 500, 700, and 1000 mL·min−1, in order to check the contact time between the dye and the electrode to evaluate the percentage of removal of RYD through photovoltaic live connection.

The electrodes were treated by rinsing them with a 1 M HCl solution and distilled water at the end of each test.

2.7. Photovoltaic Array

The photovoltaic array consisted of two Siemens Solar photovoltaic (PV) modules Solar 75 Wp, SP-75. The solar module characteristics were verified using the I-V Checker MP140 Portable PV Device Evaluation Instrument, for which the PV module was first determined, and afterwards, with two PV modules connected in parallel [8], the short circuit current increases with the number of modules connected in parallel. The experiments were carried out at the Institute of Electrical Research (latitude 18°5240.99 N, longitude 99°13 6.89 O, inclination 19°, and south oriented).

Table 2 shows the PV module characterization for one and two PV modules connected in parallel. If one solar module is considered, the acquired current is 3.8 A and is sufficient to obtain similar removal results as accomplished by the power source. In the case of a cloudy day where there is low solar radiation, the application of two modules would be required. Parallel-connected solar PV modules would offer a required minimum current intensity in the reaction performance with reasonable efficiency. The calibration of both modules set in parallel array produces a current intensity of 7.9 A.

Table 2: Characterization of solar PV modules.

3. Results and Discussion

3.1. Batch Tests with Artificial Power Source

Table 3 shows that COD removal is time dependent while applying different current intensities. At lower current intensity, the removal efficiency of COD is higher; this variation can be attributed to an interference during COD determination caused by the presence of aluminum ions when applying more current. The electrochemical reaction will produce a higher number of aluminum ions, and this explains why the removal efficiency decreases during the treatment time.

Table 3: Removal efficiency of COD mg·L−1 by different current intensities.

It is known that the current intensity applied to the system determines the amount of released ions and therefore the amount of the resulting coagulant. Thus, the higher the amount of dissolved Al3+ ions in a solution, the greater the rate of Al(OH)3 formation, and consequently a higher COD removal efficiency is expected to be achieved. In addition, the increase of current density promotes the generation of H2 bubbles and decreases its size, which should lead to a higher removal of pollutants by flotation. However, higher current values may promote a higher turbulence in the system, and consequently, the particles responsible for coagulation do not have enough time to agglomerate themselves and remove the pollutants [27] as stated by Fajardo et al. (2015).

The ions generated in the electrode are Al(aq)3+ and OH; the combination of these ions is expected to form various monomeric species such as Al(OH)2+, Al(OH)2+, Al2(OH)24+, and Al(OH)4 and polymeric species such as Al6(OH)153+, Al7(OH)174+, Al8(OH)204+, Al13(OH)345+, and Al13(OH)372+ [23, 24]. By relating these species with the report about super-faradaic efficiencies [28, 29], they are more significant at low current densities, that is, 1.75 mA·cm−2. In the case of aluminum, experimental results are significantly over the expected values for a 100%-efficiency process according to Faraday’s law, (3). This super-faradaic efficiency is explained in terms of a chemical dissolution process, which corresponds to the oxidation of the aluminum sheets with the simultaneous reduction of water to form hydrogen. It has also been mentioned that the amount of generated aluminum seems to depend on the pH, and this has been explained in terms of chemical dissolution of the aluminum electrode. In this case, the pH was initially between 5.6 and 6.3. However, it was observed that as current increases, pH rapidly decreases. For example, at I = 4, 6, 8, and 10 A, the pH was 4.8, 2.3, 2.2, and 1, respectively. Gu et al. suggest that (4) and (5) for the oxidation of water will decrease solution pH [30] and this was observed in this work, so, the super-faradaic efficiencies are greater for aluminum than those for iron [29].

The pKa of the remazol yellow dye is 3.77. Therefore, above this pH, the species of ionic form will be found, and its chromophore groups will be negatively charged. When the removal efficiency decreases, it is suggested that the precipitated hydroxide metal may have tended to dissolve in liquid thus adversely affecting the performance of the process. This fact may take place as the medium turns extremely acidic or alkaline as previously reported [3133]. The cationic metal species are responsible for the destabilization of the particles (charge neutralization), leading to the formation of flocculating particles, which will have the power to sediment contaminants [33]. In situ generation of coagulants has the advantage of reducing the amount of chemical reagents introduced into the system; however, this may lead to a change in pH. In this context, the pH of the batch tests has been reported acidic and in the continuous tests, the pH fluctuated between 7.8 and 8.9, so the predominant reaction will be represented by (3) [29].

According to the diagram of Pourbaix [34], at pH less than 4, Al3+ ions are expected, and between 4 and 8, there may be passivation by Al2O3. For this study, however, it is observed that the pH and therefore the predominant reactions depend on the flow regime, that is, in batch tests, an acidic pH is observed and (4) and (5) predominate, and in tests under continuous flow, the pH is between neutral and slightly alkaline, and without considering the effect of passivation, (3) is the predominant one as already mentioned.

Another phenomenon is the production of aluminum, so in Table 3, there is an increase of COD, although the color tends to decrease. As it is known, this production is a function of the applied current. Thus, considering the electrode area (0.44 m2) and applying Faraday’s law (6), the following values of Al3+ are calculated, 0.32, 0.48, 0.64, and 0.81 g, for currents of 4, 6, 8, and 10 A, accordingly. It is possible to have an excess of ions and for this reason, the COD value does not fall [5]. where n is the metal (), M molecular mass of electrode, I current intensity, t operating time, number of electron transferred, and F Faraday’s constant (96,500 C/mol).

In the case of aluminum, experimental results are significantly over the expected values for a 100%-efficiency process according to Faraday’s law. This super-faradaic efficiency is explained in terms of a chemical dissolution process, which corresponds to the oxidation of the aluminum sheets with the simultaneous reduction of water to form hydrogen, according to (3) [29].

3.2. Optimization of the Applied Current with the Power Source

According to the results of Table 3, the applied current must be less than 6 A; so for these tests, currents to be evaluated were selected from 2, 3, 4, and 5 A. Figure 2 shows the dye removal percentage at these current intensities where a significant difference does not appear when applying 2, 3, or 4 A, as compared to 5 A ANOVA and Duncan test () [35].

Figure 2: Removal of RYD at different current intensities: 2 A, 3 A, 4 A, and 5 A.

Figure 3 shows the dye color removal percentage at the same currents; these current intensities have the same behavior as in the removal of dye concentration.

Figure 3: Color removal at different current intensities: 2 A, 3 A, 4 A, and 5 A.

In Figures 2 and 3, a similar behavior is observed regarding the elimination of the dye elaborated with the UV-Vis spectrophotometer and the elimination of the color; they have very similar efficiencies. When performing the ANOVA, it is similar to the dye efficiency tests that with a current of 2, 3, and 4 A, there is no significant difference in the results and with respect to 5 A, if there is a significant difference ().

3.3. Batch Examinations with PV Modules

Table 1 shows that one PV module is enough to generate a current of 4 A under good solar radiation conditions, and two solar PV modules in parallel array are capable to generate 7.9 A. This means that in cloudy weather conditions, the current generated by two solar PV modules must be in the necessary range to carry out the RYD removal tests. Then, under this assumption, Figure 4 shows the comparison for RYD removal with the power source in 3 A and 4 A and one solar PV module. During this testing period, the solar PV module had an average solar radiation of 747 W/m2 and a current of 3.1 A, with an average voltage of 2.37 V; the pH dropped slightly from 8 to 6.5 units, while the temperature in the electrocoagulation reactor increased from 18.5 to 20°C. As shown in Figure 4, there are no differences in the RYD results from the power source and solar PV modules. Observing that the removal efficiency is lower for 5 A, it is established that the appropriate conditions for the work of the system with the solar panel will be sufficient if it reaches between 2 and 4 A of current. This will depend on the solar irradiation of the moment; since the solar modules are connected directly, the solar irradiation impacts directly to the electrochemical reactor, generating greater or less quantity of ions to participate in the electrocoagulation. If there is a sunny and cloudless day, adequate solar radiation is guaranteed, which is why 1 or 2 photovoltaic panels are used. This is a complement of Figures 2 and 3 where we observe the similarity in the color and concentration removals of the RYD, and if we contrast this with Figure 4 which is already an experimental process, it is possible to use one or two photovoltaic modules, considering the use of only one module for the conditions treated in these experiments.

Figure 4: Comparison between current intensity controlled with the power source and one module solar: 4 A, 3 A, and PV module.
3.4. Examination in Continuous Flow Rate

Figure 5 shows how the removal of the dye and color removal (65–70%) are kept constant in the test from 1.5 hours and onwards with a flow rate of 300 mL·min−1 and the PV current supplied by either one or two PV modules. Contrasting this graph with Figure 6, the radiation in either case, with one and two photovoltaic modules, can be observed. It is worth noting that there is a significant variation with the use of two photovoltaic modules. This can be ascribed to the day being cloudy and although it worked with the two modules reaching currents from 3.08 to 7.93 and 0.78 to 3.92 with one module, a variation is reflected although in an appropriate range for the minimum current needed for the electrochemical process. Thus, the use of two modules allows to attain currents higher than 3 A at all times. According to Figure 4, this value is sufficient for the process to occur. When only one module is used, the current will depend on the daytime and the variation may be rather rapid. For example, at 9:00 in the morning, a 0.78 A current was obtained, while 50 minutes later, the measured current was already 2 A. This trend usually prevails until 15: h. On the other hand, when two solar modules are used, the minimum attained current is 3.08 A, and between 10:00 and 15:30, the current is always higher than 3 A. Therefore, it can be concluded that two modules will always provide the adequate current regardless of the solar radiation intensity during daytime.

Figure 5: Remazol removal and color removal under continuous flow with the application of photovoltaic modules: liquid flow rate: 300 mL·min−1; initial concentration of RYD: 100 mg·L−1. % RYD one PV module, % RYD one PV module, color one PV module, and color two PV module.
Figure 6: Solar irradiation profiles as function of time: SR one PV module, SR two PV module, current one PV module, and current two PV module.

The tests by different flow rates are shown in Figure 7. As it can be observed, the differences of the dye removal efficiencies are not significant for flow rates of 500, 700, and 1000 mL·min−1; however, at 300 mL·min−1 flow rate, the difference is around 20% [36, 37]. This effect was expected since lower flow rates also imply higher residence time. It can be concluded that RYD removal efficiency is favored when the retention time, electric current, and flow rate are low [38, 39].

Figure 7: Effect of removal percentage rate on RYD initial concentration remazol 100 mg·L−1: % RYD 300 mL·min−1, % RYD 500 mL·min−1, % RYD 700 mL·min−1, and % RYD 1000 mL·min−1.

Table 4 shows the average, maximum, and minimum values of solar radiation, current intensity, and voltage for the accomplished tests by different flow rates comparing each one of 300 mL·min−1 with the remaining other. It is possible to observe that the current intensity is lower at 300 and 500 mL·min−1; however, the removal efficiency is better in the low flow rate. This proves that current above 5 A does not increase the removal efficiency.

Table 4: Evaluated parameters during different RYD flow rate.

As shown, there is variation in the current intensity for each test, because it is not possible to compare them, however, since they are connected live; it depends on the solar radiation received on the day of the test; it can only be confirmed that it will be necessary to modify the water flow rate according to the received radiation so that it is proportional to what is reported in the literature as suitable to produce the amount of aluminum to react with the dye; nevertheless, it should not be forgotten that the phenomenon of super-faradaic production of the ion that helps the dye removal is also present. Under continuous flow, there is a synergy during treatment since after 1 hour of treatment, a stationary state is reached and a dye removal efficiency of 70% is attained. Worth noticing is that this value is kept constant until the treatment is complete (Figure 4). It is considered that it is necessary to establish a chain of batteries that are charged with photovoltaic energy to be able to carry out the elimination of pollutants continuously throughout the day, without being contingent to the solar radiation. That is, to store the energy and use it at the moment that it is required.

3.5. Energy Consumption

Figure 8 shows the energy consumption to remove 1 g of RYD by means of direct current and photovoltaic current at a flow rate of 300 mL·min−1. It can be seen that under controlled current supply with a DC power system, the energy consumption to remove RYD was constant and linear, 5.38 Wh·g−1.

Figure 8: Comparison between CD and PV module.

For RYD removal by means of PV current, this was dependent on solar radiation, reaching a maximum value of solar radiation around 1:00 p.m. and descended to the lowest value by the sunset.

Valero et al. [39, 40] demonstrated that the use of photovoltaic energy (i) reduces the cost of investment by avoiding the use of batteries, solar inverters, and power supplies and (ii) reduces the cost of maintenance, since there is no waste of batteries to properly dispose.

However, the disadvantage of this process is that in Mexico, it could only be applied from 9:30 am to 4:00 p.m., since it is the time in which there is adequate solar radiation in a sunny day. Sunny days are not constant through the year though. In order to overcome this, the use of hybrid energies combining solar photovoltaic with wind could be considered. This approach, however, should be evaluated taking into account that the increase of air is in the evening, so the working hours of an electrochemical reactor can be increased [41], considering the proposal of [39].

According to Figure 8, energy consumption to remove RYD color was dependent on the generated current by one or two PV modules. However, at the highest energy consumption, RYD color removal shows a decay behavior due probably to a passivation phenomenon of the aluminum electrodes (see Section 3.1) and the consequent rising of electrical resistance thus causing the energy consumption increase.

Results reported at industrial scale show a parallel and series arrangement of the photovoltaic modules in order to obtain the electric current for the wastewater pollutant removal. However, the conditions of the photovoltaic arrangement will depend on the climatic conditions [40]. The setup for the pilot reactor of this work was two-module photovoltaic in parallel for a cloudy day and one-module photovoltaic for a sunny day.

Finally, regarding the PV energy costs, it will be possible to get a PV system at a low cost for the wastewater treatment. “Production costs for industry-leading Chinese crystalline-silicon (c-Si) PV module manufacturers -- such as Jinko Solar, Renesola, Trina Solar and Yingli Green Energy -- will fall from 50 cents per watt in the fourth quarter of 2012 to 36 cents per watt by the end of 2017,” according to a new report from GTM Research. The report, PV Technology and Cost Outlook, 2013-2017 [42], predicts that the majority of these cost declines will derive from technology innovations such as diamond wire sawing for PV wafers, advanced metallization solutions, and increased automation in place of manual labor.

4. Conclusions

It is possible to use the photovoltaic modules to conduct wastewater treatment by electrocoagulation. In this work, the highest attained removal efficiency of RYD and color were 70% for both under continuous flow. The achieved current from one PV module was enough to generate electrocoagulation and remove RYD and color in a sunny day or two PV modules in parallel on a cloudy day. In order to obtain the electrocoagulation reaction, the current intensity should be between 3 and 4 A. The recommended operation flow rate in the system is 300 mL·min−1; if the flow rate is increased, the removal efficiency decreases.

It is important to take into account the costs and the innovation in photovoltaics, since its implementation for scaling will depend on these, as well as on being able to install a complete system for storing solar energy and control the power to the system, always looking for the better pollutant removal efficiencies.

Conflicts of Interest

The authors declare that they have no conflicts of interest.

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