Electroosmotic dewatering of cellulose nanocrystals
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One of the main challenges for industrial production of cellulose nanocrystals is the high energy demand during the dewatering of dilute aqueous suspensions. It is addressed in this study by utilising electroosmotic dewatering to increase the solid content of suspensions of cellulose nanocrystals. The solid content was increased from 2.3 up to 15.3 wt%, i.e. removal of more than 85% of all the water present in the system, at a much lower energy demand than that of thermal drying. Increasing the strength of the electric field increased not only the dewatering rate but also the specific energy demand of the dewatering operation: the electric field strength used in potential industrial applications is thus a trade-off between the rate of dewatering and the energy demand. Additionally, it was found that high local current intensity had the potential of degrading cellulose nanocrystals in contact with the anode. The maximum strength of the electric field applied should therefore be limited depending on the equipment design and the suspension conditions.
KeywordsCellulose nanocrystals Nanocellulose Electroosmotic dewatering Solid–liquid separation Energy demand
Production of cellulose nanocrystals and nanofibrillated cellulose is gathering significant interest amongst researchers as these materials combine mechanical strength and toughness with a low density, biodegradability and renewability (Siró and Plackett 2010). Applications in which they may be used are therefore plentiful, either as components in composite materials or in films and foams (Isogai 2013). However, large-scale production of materials based on cellulose nanocrystals requires the development of processing techniques that are industrially viable (Oksman et al. 2016). Cellulose nanocrystals are typically produced and processed in aqueous suspensions, so one of the main challenges facing the large-scale production of materials from cellulose nanocrystals is therefore to obtain an energy-efficient solid–liquid separation.
Production of cellulose nanocrystals through acid hydrolysis typically results in the formation of suspensions with a low solid content. On a laboratory scale, centrifugation is often used to increase the solid content during washing of the particles, however, the solid content is typically remains in the range 0.2–3 wt% (e.g. Ávila Ramírez et al. 2017; Bai et al. 2009; Cranston and Gray 2006; Kedzior et al. 2016). Many industrial applications require that this solid content is increased and different drying methods, such as thermal, freeze and supercritical drying, can be used to obtain a dry material (Peng et al. 2012, 2013). However, these techniques are associated with significant energy demands. Dewatering will therefore have a great influence on the energy demand of industrial production of cellulose nanocrystals. A rough estimate of the energy demand for drying can be made from the amount of water that needs to be separated: the heat of evaporation of water is 2260 kJ/kg at atmospheric pressure and, assuming an initial solid content of the suspension of 2 wt%, the resulting energy demand would be about 110 MJ/kg of dry cellulose nanocrystals. Increasing the solid content of the suspension before drying could therefore decrease the energy demand in large-scale production to a very large extent.
The solid content is often increased by a mechanical dewatering operation such as filtration as a precursor to drying operations. However, the large specific surface area of cellulose nanocrystals means that the filtration resistance of the material is very high; the demands this makes on operation time and/or equipment size therefore limits the use of filtration. Electroosmotic dewatering is an assisted filtration technique that can be used to increase the solid content of suspensions of materials with charged surfaces (Iwata et al. 2013; Mahmoud et al. 2010). It has proved to be useful in increasing the solid content of cellulosic materials with high specific surface areas (Wetterling et al. 2017a), such as microfibrillated cellulose suspensions (Heiskanen et al. 2014), and has also shown potential for use in the dewatering of both biopolymers (Gözke and Posten 2010; Hofmann et al. 2006; Hofmann and Posten 2003) and hydrogels (Tanaka et al. 2014). Using electroosmotic dewatering prior to drying can decrease the total energy demand of the dewatering operation (Larue et al. 2006; Loginov et al. 2013; Mahmoud et al. 2011) and is therefore also attracting significant research interest in the treatment of wastewater sludge (Citeau et al. 2012; Mahmoud et al. 2011; Olivier et al. 2015).
In this study, the use of electroosmotic dewatering to increase the solid content of suspensions of cellulose nanocrystals is investigated. The manner in which the strength of the applied electric field influences the dewatering operation is studied with regard to the dewatering rate as well as the specific energy demand.
Preparation of the cellulose nanocrystals
Suspensions of cellulose nanocrystals were prepared by acid hydrolysis of a commercially available microcrystalline cellulose (Avicel® PH-101) using a procedure described in an earlier publication (Sahlin et al. 2017) adapted from Hasani et al. (2008). Hydrolysis of 500 g microcrystalline cellulose was performed using 4.37 dm3 of 64% w/w sulphuric acid at 45 °C for 2 h under continuous stirring, after which the suspension was diluted with deionised water to quench the reaction. Excess acid was removed through dialysis against deionised water until the conductivity of the effluent was stable, below 5 µS/cm. The suspension was then sonicated using a Vibracell Sonicator (Sonics and Materials Inc., Danbury, CT) at 40% output for 6 × 7 min until a colloidal dispersion of cellulose nanocrystals was obtained.
The prepared suspension of cellulose nanocrystals had a cellulose content of 2.3 wt%, a pH of 3.3 and a conductivity of 1950 μS/cm. The prepared suspension was stable, neither precipitate nor supernatant was observed after centrifugation (4000×g for 15 min).
Characterisation of the cellulose nanocrystals
Cellulose nanocrystals produced using the same setup and procedure as used in this study have been characterised extensively in a previous publications; the average dimensions of the dispersed cellulose nanocrystals were determined as being ~ 300 nm × 7 nm by atomic force microscopy (Börjesson et al. 2018; Moberg et al. 2017).
The use of sulphuric acid in the hydrolysis of cellulose introduces negatively charged sulphate half-ester groups on the surface of the cellulose nanocrystals and affects the charge of the particle surfaces (Beck-Candanedo et al. 2005). The content of sulphate esters was determined by conductometric titration with 0.01 M sodium hydroxide at a cellulose content of 0.1 wt% in the suspension. The content of sulphate was determined at 350 μmol/g cellulose. The ζ-potential of the cellulose nanocrystals was measured under controlled conditions using a Zetasizer Nano ZS (Malvern Instruments). Samples were diluted to a solid content of 0.05 wt% and the pH adjusted to 3.5, followed by ion exchange (Dowex Marathon MR-3 hydrogen and hydroxide form) and subsequent removal of the resin beads through filtration. Repeated measurements were performed at 25 °C and the ζ-potential was determined as − 72(± 2) mV.
Cellulose nanocrystals were examined after electroosmotic dewatering using Fourier Transform Infrared (FT-IR) spectroscopy (PerkinElmer Frontier) with an Attenuated Total Reflectance (ATR) sampling accessory (PIKE Technologies GladiATR). Samples were measured with a resolution of 4 cm−1 and 32 scans; all spectra were corrected against air and normalised to the highest band.
Electroosmotic dewatering equipment
The dewatering cell is equipped with two platinum electrodes connected to a DC power supply (EA-PSI 5200-02 A, Elektro-Automatik). An expanded platinum mesh (Unimesh 300) is used as the cathode and is placed beneath the filter medium. The anode, which is a mesh made of platinum wire of diameter 0.127 mm, has 10 mm square openings. The anode is placed inside the dewatering cell resting on a support rack; the internal diameter of the cell is thus decreased to 50 mm for the 30 mm closest to the filter medium. The electrode separation is constant at 25 mm; a constant voltage is applied during each dewatering experiment.
In the region between the electrodes an electrophoretic force acts on the cellulose nanocrystals in the direction of the anode, whereas water is transported by electroosmotic flow through the filter cell and collected beneath the cathode. As water is being removed from the system through the filter medium, the suspension enters the space between the electrodes through the openings in the anode mesh. The volume of the dewatering cell above the anode thus acts as a reservoir, feeding suspension into the volume between the electrodes.
Results and discussion
The influence of the strength of the electric field on the dewatering rate and the specific energy demand of the operation is discussed in the following sections.
Strength of the electric field
Figure 3 shows that when an electric field of 5 V/cm was applied, the dewatering rate was fairly stable up to a solid content of 10 wt%. Doubling the strength of the applied electric field to 10 V/cm resulted in a doubled dewatering rate, as would be expected according to the Helmholtz-Smoluchowski equation. At these applied electric field strengths, Fig. 4 shows that the current intensity increased during the dewatering operation: an effect of the increasing electrical conductivity of the system. The electrical conductivity increased due to a combination of the accumulation of ionic electrolysis products between the electrodes and the increasing content of cellulose nanocrystals enhancing the contribution of surface conductivity.
As the average solid content between the electrodes approached, or surpassed, 10 wt% both the dewatering rate and the current intensity decreased for the experiments performed at 5 and 10 V/cm. A possible explanation for this effect could be that the solid gel structure of the cellulose nanocrystals at these solid contents decreases the flow of the suspension through the anode mesh, thereby resulting in desiccation of the cellulose nanocrystals that are in contact with the anode. Desiccation would result in a decrease in electrical conductivity and cause a high voltage drop close to the anode: the strength of the electric field in the rest of the filter cell would be lowered and thus reduce the driving force for electroosmotic flow. Further studies, using anodes of different designs and various cell configurations, are required to investigate this behaviour.
At an applied electric field of 15 V/cm the relation between the initial dewatering rate in Fig. 3 and the rates at 5 and 10 V/cm was as expected, according to the Helmholtz–Smoluchowski equation: a linear dependence on the strength of the electric field applied. For an applied field of 15 V/cm, however, the dewatering rate decreased at a solid content of about 6 wt% to a rate lower than that obtained for 10 V/cm. The current intensity in Fig. 4 increased with the solid content in a similar manner as for the lower electric field strengths up until 6 wt%. However, when the current intensity approached 220 A/m2, the intensity of the current decreased rapidly, indicating an increase in electrical resistance. It should be noted here that the intensity of the local current at the anode wire was significantly higher, due to the design of the electrode employed. Dissection of the gel of cellulose nanocrystals obtained after electroosmotic dewatering showed the formation of a black layer, possibly char, in the immediate proximity of the anode wire. A reasonable explanation for the increasing electrical resistance is thus the formation of the char layer. The char layer and the suspension of cellulose nanocrystals present between the electrodes may then be considered as being two electrical resistances coupled in series. A char layer of high electrical resistance will give a significant voltage drop close to the anode and decrease the strength of the electric field in the remainder of the filter cell which, in turn, will decrease the driving force of electroosmotic flow.
Specific energy demand
The energy demand of the electroosmotic dewatering of suspensions of cellulose nanocrystals using the experimental setup in this study was only a fraction of that required for thermal drying: for reference, the heat of evaporation of water at atmospheric pressure is 0.63 kW h/kg. The energy demand of the electroosmotic dewatering operation is, however, influenced by the electrical conductivity of the suspension. The energy demand of systems with a high degree of electrical conductivity, e.g. suspensions of high ionic strength, will increase as the intensity of the current required to maintain the electric field increases (Wetterling et al. 2017a). Moreover, the energy demand will also be influenced by the electrode separation as this influences the electrical resistance of the system and the strength of the electric field for any given voltage that is applied.
Electroosmotic dewatering can be used to increase the solid content in suspensions of cellulose nanocrystals. Using the experimental equipment presented in this study the solid content of a suspension of cellulose nanocrystals was increased from 2.3 to 15.3 wt%: this corresponds to the removal of more than 85% of all water present in the initial suspension at a very low energy demand compared to thermal drying.
Increasing the strength of the electric field increased the rate of dewatering, but also increased the energy demand of the dewatering operation.
Increasing the electric field strength above 10 V/cm for the experimental equipment and suspension of cellulose nanocrystals used in this study gave had no positive effect on the dewatering rate yield due to a layer of degraded cellulose formed in direct contact with the anode.
This study was performed within the framework of the Wallenberg Wood Science Center, and the financial support of the Knut and Alice Wallenberg Foundation is gratefully acknowledged. Maria Gunnarsson is thanked for her assistance with the IR spectroscopy.
- Heiskanen I, Backfolk K, Kotilainen A, Gaidelis V, Sidaravicius J (2014) Process for treating microfibrillated cellulose and microfibrillated cellulose treated according to the process. US Patent 2014/0088301 A1Google Scholar
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