1.1 General
Due to the population explosion and rise in the standard of living, the demand for freshwater is increasing rapidly (Elimelech & Phillip, 2011; Ward & Pulido-Velazquez, 2008). Knowing the issues with the availability of conventional water resources and wastewater effluent disposal standards, the reuse and recovery from wastewater is gaining impetus (Jury & Vaux, 2005; Shon et al., 2015). These non-conventional water resources provide water security and are considered a reliable alternative in many countries (Khawaji et al., 2008).
Industries consume a vast quantity of fresh water and generate a colossal amount of wastewater. The dairy industry, in particular, consumes about 1–10 m3 of water per m3 of processed milk (Wojdalski et al., 2013). The effluent of dairy primarily includes milk or milk products particles, by-products of the manufacturing process like whey, contaminants left after washing of cans, tanks, equipment, floors and after Cleaning In Place (CIP) operations (Kolev, 2017). It has high Biochemical Oxygen Demand (BOD), Chemical Oxygen Demand (COD), Total Dissolved Solids (TDS), pH and oil as well as grease. Thus letting it out without any treatment creates eutrophication in the environment(Al-Shammari et al., 2015; Kolev, 2017).
1.2 Whey
Whey is the liquid by-product generally produced during the manufacture of cheese, paneer, yogurt etc. It is the liquid remaining after the removal of fats and caseins from the milk(Wit. JN, 2001). Typically, white colour is observed for dairy wastewater and greenish yellow for whey(Duke & Vasiljevic, 2015). The global annual whey production is approximated to be over 108 tonnes per annum(Grba et al., 2002). A typical whey has approximately 93–94% water content and around 7.12 ± 0.52% of total solids content (Kolev, 2017), constituting a high percentage of lactose. In contrast, proteins, fats and salts are significantly less in composition(Healy et al., 2007). This organically loaded whey is not reused in many dairies and is just treated with dairy wastewater. It has high COD and BOD and thus creates a significant load on the dairy wastewater treatment plant(Kavacik & Topaloglu, 2010). Whey can be processed in mainly three ways— valorisation of whey to recover lactose and proteins, biological treatment and physicochemical treatment(Aydiner et al., 2013). Biological treatment, such as hydrolysis of lactose and proteins produces lactose monosaccharides (glucose and galactose), peptides and amino acids. While controlled fermentation can produce lactic acid, ethanol, and hydrogen. Physicochemical treatments include coagulation, flocculation, ozonation, oxidation, precipitation, gasification, etc (Aydiner et al., 2013, 2014). Among the various whey processing techniques stated above, membrane technologies are considered the most advanced and reliable (Haupt & Lerch, 2018; Shon et al., 2015). Since the 1960s, there has been much development in membrane technology because of the high investment in research and development for membranes (Shon et al., 2015). Membrane separation techniques such as microfiltration (MF), ultrafiltration (UF) and nanofiltration (NF) are extensively used in the dairy industry to separate various whey ingredients such as fats, proteins, lactose and minerals. Reverse Osmosis (RO) is also used for the removal of water to attain a certain Total Solids (TS) content before the concentrated stream is fed to a multiple-effect evaporator and eventually to a crystallizer to obtain the crystallized product (Wit. JN, 2001). All these membrane techniques require hydraulic pressure to operate and are also prone to membrane fouling (Shirazi et al., 2010). So the major issues which plague the membrane process are its high cost, high energy consumption and the high tendency of fouling (Shon et al., 2015).
1.3 Forward Osmosis
Amongst these prevailing expensive and energy consuming membrane technologies, Forward Osmosis (FO) is looked upon as a potential alternative in recent years to replace the costly pressure driven membrane processes (Honmane et al., 2020; Mogha, 2020). FO is another membrane-based separation technique that is a thermodynamically spontaneous process, unlike its hydraulic pressure-driven counterparts. In FO, the driving force is the high osmotic pressure (𝜋) gradient generated by the concentrated draw solution to allow fresh water to permeate through the semi-permeable membrane from the feed solution towards the draw solution (as shown in Fig. 1) (Aydiner et al., 2014; McCutcheon et al., 2005; Tang et al., 2010). The products of FO are a diluted draw solution and a concentrated feed solution (Zhao et al., 2012). The phenomenon of FO can be explained by the second law of thermodynamics. In other membrane-based techniques such as RO, entropy is lowered; hence work has to be done on the system (i.e., hydraulic pressure). But in FO, the total entropy of the system is raised; thus no hydraulic pressure is required. On the contrary, since entropy is generated in FO, some work can be extracted from the process, and that is the principle used in harnessing the salinity gradient energy, also called blue energy.
There have been a few reported works on partial dewatering of whey using FO. Using flat sheet Cellulose Triacetate (CTA) membrane of 140cm2 and RC operation mode along with 3M and 2M NaCl solution as the draw, the draw regeneration is done using RO and Membrane Distillation (MD) respectively (Aydiner et al., 2013). Using 4M NH4CO3 as the draw solution and the CTA membrane, the draw was regenerated using thermal decomposition methods(Seker et al., 2017). The RC mode has been reported with the draw solution of concentration 1M NaCl (Wang et al., 2017) along with Thin Film Composite (TFC) membrane of area 106 cm2, 60°Bx Potassium Lactate solution (Menchik & Moraru, 2019) coupled with spiral wound CTA membrane of 0.5 m 2 and 50 gL− 1 NaCl draw solution for CTA membrane of 12 m2 (Chen et al., 2019) with no draw generation has been reported. The majority of the studies have been carried out using the RC mode of operation along with no draw regeneration or regeneration using some energy-consuming techniques.
In this study, an attempt has been made to propose a continuous process to partially recover water from the dairy waste stream whey by using FO and the value addition to the draw to eliminate the need for regeneration. Sodium Chloride (NaCl) is one such solute that not only finds application in the dairy industry (Wit.J.N., 2001) as the potential brine but is also the potent osmotic agent. So, applicability of the high osmotic pressure aqueous (aq.) NaCl as the draw solution for the partial concentration of whey has been investigated. The study is a novel work carried out to compare the Continuous Single Pass (CSP) mode and Recirculation (RC) mode of FO on commercial FO membrane with an aim to achieve maximum water recovery and permeate flux. Experiments are also carried out to capture the effect of Feed/Draw (F/D) ratio on the performance of tFO process.