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Chemical structure of regenerated cellulose.

Chemical structure of regenerated cellulose.

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The effects of different parameters including membrane type (regenerated cellulose and polysulphone), transmembrane pressure (TMP), the content of oil in the feed, the flow velocity of the feed and pH on the ultrafiltration of an emulsion of kerosene in water were studied. It was found that the important factors affecting ultrafiltration were, in o...

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... high number of OH groups (Fig. 2) in regenerated cellulose membranes apparently makes these membranes very hydrophilic. Fig. 3 shows the chemical structure of polysulphone. There are no OH groups in polysulphone. Thus it is expected that the water permeation (flux) is lower than in a regenerated cellulose membrane with the same pore size while in Table 1 the water ...

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Citations

... Previously, ultrafiltration (UF) and microfiltration (MF) flat-sheet (FS) membranes for the treatment of oily wastewater have been studied for many years. For example, Rezvanpour et al. (2009) used a bench-scale cellulose UF membrane setup to treat kerosene-contaminated wastewater. The membrane filtration system was operated at a constant transmembrane pressure (TMP) of 3 bar and was able to achieve a total organic carbon (TOC) removal efficiency of 98%. ...
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... The efficiency of kerosene removal (RE%) and the quantity of kerosene adsorbed (q t ) were calculated by Equations (5) and (6), respectively [19,36]: ...
... The third kinetic model (that is, intra-particle diffusion based on the theory proposed by Weber and Morris) was used to identify the diffusion mechanism [36]. The initial rate of intra-particle diffusion is expressed by Equation (9) [64]: ...
... The pseudo-second order model has been applied in the sorption of oil and metal ions over MWCNTs [65]. The third kinetic model (that is, intra-particle diffusion based on the theory proposed by Weber and Morris) was used to identify the diffusion mechanism [36]. The initial rate of intra-particle diffusion is expressed by Equation (9) [64]: ...
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... The capacity of using a flotation is in the range of 10À500 m 3 /h. p0125 Membranes [MF (Koltuniewicz, Field, & Arnot, 1995;Hu & Scott, 2007) and UF (Chakrabarty, Ghoshal, & Purkait, 2010;Rezvanpour, Roostaazad, Hesampour, Nyströ m, & Ghotbi, 2009)] can be successfully applied as a secondary treatment to remove emulsified and dissolved oil from oily wastewater. As in all membrane technologies, both MF and UF membranes still suffer from fouling and concentration polarization caused by adsorbing oil or surfactant, which lead to a reduction in permeate flux with time (Dickhout et al., 2017b). ...
Chapter
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... Reprinted with permission from Ref. [117]. [31,95,106,158,161,173,174]. In this regard, various experimental design tools like the Taguchi method [31,173,174], response surface method (RSM) [106,158,161] adaptive neuro-fuzzy inference system (ANFIS) [95], etc. are very helpful to obtain a combined effect of the UF variables and the objective functions (Table 11). ...
... [31,95,106,158,161,173,174]. In this regard, various experimental design tools like the Taguchi method [31,173,174], response surface method (RSM) [106,158,161] adaptive neuro-fuzzy inference system (ANFIS) [95], etc. are very helpful to obtain a combined effect of the UF variables and the objective functions (Table 11). Rezvanpour et al. [173] used the Taguchi method in the optimization of membrane material (i.e., PSF, CA) and operating parameters (i.e., TMP, pH, CFV and feed oil concentration) for the treatment of kerosene-water emulsion. ...
... In this regard, various experimental design tools like the Taguchi method [31,173,174], response surface method (RSM) [106,158,161] adaptive neuro-fuzzy inference system (ANFIS) [95], etc. are very helpful to obtain a combined effect of the UF variables and the objective functions (Table 11). Rezvanpour et al. [173] used the Taguchi method in the optimization of membrane material (i.e., PSF, CA) and operating parameters (i.e., TMP, pH, CFV and feed oil concentration) for the treatment of kerosene-water emulsion. ...
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... Statistical experimental design incorporating design of experiments (DoE) techniques can be used to investigate the effects of all the possible interactions between the factors at one time, while undertaking the fewest possible experiments. A review of the literature revealed that an increasing number of studies are being conducted using DoE approaches in the membrane technology field to optimize operating conditions [10,[27][28][29][30][31][32]. The DoE approaches for robust design include the Taguchi method that combines mathematical and statistical techniques to arrive at a special design of experiments with an orthogonal array (OA) to study multiple factors with a small number of experiments. ...
... An experimental design based on the Taguchi method was used to design the experiments. The Taguchi method applies fractional experimental designs, called orthogonal arrays (OA), to reduce the number of experiments required to determine the optimum conditions based on the results [29,30,42]. One of the important steps in the Taguchi approach is the appropriate selection of OAs, which depends on the number of control factors and their levels. ...
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... Generally, permeate flux is higher at higher crossflow velocities [27][28][29][57][58][59][60] as an an increase in shear at the membrane surface mitigates fouling. In the case of individual oil droplets that block membrane pores, a detailed analysis of droplet behavior on a membrane in a crossflow-induced shear field is possible [61][62][63][64]. ...
... MF separations of oil-water emulsions have employed membranes in different configurations including: polymeric flat-sheet [13,29,71,78,[99][100][101][102][103][104][105][106][107][108][109][110][111][112][113][114][115][116][117], polymeric tubular [118][119][120][121], ceramic tubular [77,82,85,99,120,[122][123][124][125][126][127][128][129][130][131][132][133][134][135], ceramic tubular with multiple channels [136][137][138][139], ceramic flat disk [29,[72][73][74]99,140,141], hollow fiber [142][143][144], microporous glass tubular [145,146], membrane with slotted pores [93,[147][148][149][150][151], metal membrane with conical pores [152,153] and a few other specialty membranes such as silica-supported PVDF [154] and flexible TiO 2 /Fe 2 O 3 composite membranes [155]. Similarly, UF membranes used to separate oil-water emulsions included polymeric flat-sheet [58,76,77,80,[104][105][106]108,110,, polymeric tubular [189][190][191][192][193][194], ceramic tubular [77,[195][196][197][198][199], ceramic tubular with multiple channels [139,[200][201][202][203], ceramic flat disk [46] and hollow fiber [86,121,143,144,196,[204][205][206][207]. ...
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Separation of liquid-liquid emulsions is a challenging problem that has gained in importance with the development of unconventional oil resources. Large volumes of water contaminated by emulsified oil need to be treated for safe disposal or efficient reuse. Among technologies capable of removing oil dispersed into smaller size droplets (< 15 µm), membrane processes occupy a unique niche where the required separation performance and throughput can be achieved at a relatively modest cost. As with most membrane-based processes, separation of emulsified oil entails membrane fouling that requires regular maintenance and imposes additional operational costs. Emulsions present unique challenges in that their fouling behavior is affected by droplets’ deformability, coalescence both in the bulk and on the membrane surface, membrane wetting by droplets and films, pore blockage and intrusion by oil. The purpose of this paper is to overview the literature on the separation of oil-water emulsions by pressure-driven membrane processes with an emphasis on how properties of emulsions and membranes affect separation performance. A particular focus is on membrane fouling by oil including physicochemical bases, detection, diagnosis, and visualization. The review spans studies with both industrial oily wastewater and synthetic model emulsions of various types of oil. The discussion of membrane materials is limited to surface modifications that render membranes more fouling-resistant.
... For C1, the peak at 1747 cm −1 indicates the presence of C_O groups, which may due to the stretching vibrations of C_O in the carboxyl or ester groups. The peaks at 1238, 1161 and 1099 cm −1 correspond to the stretching vibrations of C\ \O in ester groups [36]. For C2, the peaks at 3458 cm −1 and 1306 cm −1 correspond to the stretching vibrations of the O\ \H bonds of the N\ \H groups. ...
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The flotation performance of lignite is poor even if a high dosage of the collector is used. In this work, the lignite in the Huolinhe Coalfield of Inner Mongolia was used, and its physicochemical properties were determined by proximate analysis, particle size analysis and Fourier transform infrared spectroscopy. The flotation performances of lignite using six collectors were investigated. Moreover, the flotation responses of lignite with combined collector and two emulsified collectors were compared. It was found that the polar groups in the collector structure were helpful to improve the flotation of lignite through reducing the induction time to 15 ms, only 1/12 of that of the traditional collector (190 ms for diesel). The induction time was in the order of diesel> kerosene> emulsified kerosene> emulsified diesel> C1 (one of the nameless collectors), consistent with the flotation performance. C1 and emulsified collectors significantly improved the flotation performance of lignite by promoting the floating of coarse coal (−500 + 250 μm).
... Petroleum refining industries use large amounts of water for diverse processes and thus generate a huge volume of wastewater which needs to be properly treated before it could be discharged. The conventional chemical methods such as adsorption, gravity separation, filtration, coagulation and coalescence that are frequently applied in water treatment plants to treat refinery wastewater are disadvantageous due to high operation costs, low treatment efficiency, corrosion, recontamination problems, etc. [5]. On the other hand, biological treatment methods can overcome these drawbacks. ...
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Rapid consumption of fossil fuels has led to the search for alternative energy sources. Bio-fuels as an alternative energy source require cheap and abundantly available substrates to keep the economics of the production process low. The present study was therefore focused on utilizing raw refinery wastewater by the oleaginous bacterium Rhodococcus opacus for converting it into bio-oil via hydrothermal liquefaction of the lipid rich biomass produced during the treatment process. For treating the wastewater, different operating modes using a bioreactor were evaluated including batch, fed-batch, sequential batch, continuous and continuous with cell recycle using low cost tubular ceramic membrane. Among the different strategies, the continuous cell recycle system proved efficient in terms of complete removal of chemical oxygen demand (COD) (99%) and high lipid production (86%, w/w) at a hydraulic retention time (HRT) of 16 h (dilution rate of 0.06 h ⁻¹ ). Furthermore, the residual bacterial biomass from the bioreactor was treated by HTL to produce bio-oil which showed excellent bio-fuel properties. This study demonstrated the application of R. opacus for simultaneous wastewater treatment and production of bio-oil for energy application.
... Effect of TMP on permeate flux (given by Eq. (6)) is explained as follows: initially, with increasing the pressure, the transmembrane flux also increases until a maximum flux is reached, due to an increase in the driving force across the membrane; further increase of pressure then causes the flux to decrease until the flux becomes independent of pressure. The collapse of flux with increasing pressure is because of the enhanced resistance of the thickening gel layer (as a result of concentration polarization) formed by further accumulation of solute on the membrane surface and also the penetration of larger number of droplets into the membrane pores evincing pore plugging at a faster rate; however, once the solute's convective mass transfer to the membrane surface is balanced by its diffusive flow back to the bulk solution, the permeate flux has attained steady state condition at which it is unfettered by pressure and is solely controlled by the rate of backward diffusive transport from its surface to the solution [192,205,[207][208][209] ...
... Superior flux stability may be achieved by modification of membrane operating conditions, such as cross-flow velocity, TMP, and feed temperature [198,210]. Larger permeate flux has been observed for membranes with higher surface porosity (more number of pores), larger pore size, lower feed oil concentration, greater hydrophilicity, intermittent operation, higher temperature, and/or enhanced cross-flow rate (CFR) [190,194,198,208,209]. Nevertheless, increasing CFR at constant TMP diminishes the percentage of oil rejection because the oil droplets are fragmented at higher CFR, ending in oil diffusion into the pores together with permeate. ...
... Surface coating of membrane applied to tune its hydrophilicity and change of the operation mode (e.g., from parallel-flow to crossflow ) are the means reported to minimize/eliminate the fouling effect [210,212]. However, high hydrophilicity of a membrane for breakup of an O/W emulsion, for instance, may not always guarantee its lack of fouling by oil droplets [208]. ...
... Current methods for treatment of API separator effluent of Tehran refinery do not meet the minimum standards to be reused at boilers and cooling towers or to be discharged to the environment. In this research, to achieve high rejection and permeate flux, effects of four operating parameters, i.e., trans-membrane pressure, backwash time, temperature, and cross flow velocity (or flow rate) in a pilot setup were studied using statistic method or called Taguchi experimental design method that available in literatures151617181920212223. ...
... This software calculated the S/N ratios. Finally, the optimal operating conditions were chosen based on these ratios as illustrated in previous studies [23, 25]. Temperature (T), trans-membrane pressure (TMP), cross flow velocity (CFV), and backwash time (BWT) (at three levels) for MF and UF (PVC) membranes; three factors for UF (PAN) and RO membranes which are T, TMP, and flow rate (Q) (at three levels) are studied in our 12 investigation on the fluxes and rejection of membranes. ...
Research
This paper is accepted by Journal of Water Chemistry & Technology and it will be published at the end of 2017. Manouchehr Nadjafi is first author and Professor Al Arni from King Saud University is third and Corresponding author.