Rheological characterization of thermal hydrolysed waste activated sludge
Graphical abstract
Introduction
Thermal hydrolysis (TH) is a processing technique involving usage of high temperatures (100–200 °C) to achieve desirable physical or chemical changes in wastewater sludge. One major application is in anaerobic digestion, where TH is used as pre-treatment to overcome the rate-limiting hydrolysis step, showing favourable results and successful industrial-scale application (Barber, 2016; Carrère et al., 2010; Sapkaite et al., 2017; Zhen et al., 2017). In these processes, particulate organic matter is solubilized through application of heat for a defined period. This disintegrates cellular material to release organic compounds, which improves microorganism access to them, thus enhancing anaerobic digestion performance (Ariunbaatar et al., 2014; Suárez-Iglesias et al., 2017). Besides that, TH leads to advantageous rheological enhancements. For example, the viscosity of thermally-treated sludge is greatly reduced, which improves the efficiency of pumping, mixing, heating, digester loading, and sludge dewaterability (Farno et al., 2017; Morgan-Sagastume et al., 2011; Pérez-Elvira et al., 2008; Pérez-Elvira and Fdz-Polanco, 2012; Zhou et al., 2013). Rheology plays an important role in the design and operation of sludge handling systems (Dentel, 1997; Eshtiaghi et al., 2013). Despite extensive research on sludge TH, detailed studies related to its rheology are scarce (Barber, 2016). Accordingly, detailed characterization of sludge flow behaviour during TH and its viscoelastic properties is of interest and can lead to better implementation of TH processes.
Waste activated sludge (WAS) is the main sludge-type handled in TH processes; its rheology at ambient conditions has been well researched (Eshtiaghi et al., 2013; Ratkovich et al., 2013). WAS rheology is generally accepted to behave as a non-Newtonian, shear-thinning fluid, commonly described by the Herschel-Bulkley model. It exhibits thixotropic properties (Guibaud et al., 2004) and many studies identified the presence of yield stress (Farno et al., 2015; Markis et al., 2014; Ratkovich et al., 2013). Besides, WAS exhibits viscoelasticity, meaning that it initially shows solid-like behaviour under stress but liquid-like behaviour upon breakdown of floc structure. Furthermore, the rheological properties of WAS become more significant at high solids concentrations.
A few studies described the flow behaviour of WAS after TH. Herschel-Bulkley flow behaviour has been reported (170 °C, 60 min TH, for 5.4–18.7 wt% WAS) (Feng et al., 2014a) but Newtonian behaviour was also reported, such as Feng et al. (2014b) (170 °C, 60 min TH, for 5.4 wt% WAS) and Urrea et al. (2015) (160–200 °C TH of 2.3 wt% WAS). However, these studies were mainly concerned with post-thermally treated sludge measured at ambient conditions, which can deviate by up to 80% compared to in-situ measurements (Hii et al., 2017). In-situ characterization of WAS flow behaviour has been shown by Farno et al. (2016a), who reported the apparent viscosity and Herschel-Bulkley parameters were dependent on treatment duration and temperature. However, their study was limited to low temperature thermal processes (50–80 °C, 1 h). Recently (Hii et al., 2017), characterized in-situ WAS flow behaviour (80–145 °C, 1 h TH), but was limited to one concentration of sludge. Due to viscosity reduction, higher concentrations of feed sludge are desirable in TH, allowing higher organic loading rates in anaerobic digesters (Morgan-Sagastume et al., 2011). Then, its impact on TH rheology must be considered.
For untreated sludge, the effect of solids concentration on sludge viscosity and consistency index has been shown following an exponential function (Guibaud et al., 2004; Markis et al., 2014; Sanin, 2002; Tixier et al., 2003) or power-law model (Lotito et al., 1997; Markis et al., 2014). Whereas yield stress follows exponential (Guibaud et al., 2004; Mori et al., 2006) or power-law relationship (Forster, 2002; Lotito et al., 1997; Markis et al., 2014). For thermally treated WAS, an exponential relationship has been described for apparent viscosity and consistency index (Feng et al., 2014a). In another study, yield stress has been described following exponential relationship with concentration, whereas the consistency index and flow index followed a polynomial function of third and second order, respectively (Urrea et al., 2015). However, it has not been shown whether the same relationship exists during TH.
Viscoelastic properties have been reported for thermally treated WAS. Generally, the storage (G′) and loss moduli (G″) reduced as a result of TH, and G’>G” (Farno et al., 2016a; Feng et al., 2014a; Zhang et al., 2017), although some studies also suggest G”>G’ at low concentrations (<0.8 wt%) (Feng et al., 2014a, 2014b). However, Feng et al. (2014a) and Feng et al. (2014b) did not examine the impact of varying treatment temperature whereas Farno et al. (2016b) was related to low temperature (50–80 °C) thermal sludge processing. Zhang et al. (2017) characterized the viscoelastic properties of WAS (14.2 and 18.2 wt%) after low (60–90 °C) and high temperature (120–180 °C) TH. A Kay-Bernstein-Kearsley-Zappa (KBKZ) model described the viscoelastic properties. However, their study was concerned with polyacrylamide (PAM) conditioned sludge, which alters flocculation and network structure. Furthermore, Farno et al. (2018) have shown that a fractional derivatives Kelvin-Voigt model was more representative for sludge viscoelasticity but was limited to lower thermal treatment temperatures (<80 °C) and sludge concentrations (<6.1 wt%).
The current study expands the in-situ rheological characterization of WAS during TH for various sludge concentrations, evaluating the impact of sludge concentration, temperature and treatment time. Empirical equations are derived describing changes in the apparent viscosity, yield stress, and consistency index during TH at various sludge concentrations. Furthermore, the viscoelastic properties of the raw and thermally-treated WAS are investigated. The results from viscoelastic measurements are fitted to a fractional derivates Kelvin-Voigt model, which has not been attempted before for high-temperature thermally treated sludge. Finally, the adaptability of dynamic measurements to obtaining steady shear data is evaluated, assessing its potential for overcoming the practical challenges related to the steady shear flow measurement of highly concentred sludge.
Section snippets
Waste activated sludge
Samples of WAS were collected at initial solids concentration 3.5 wt% from Mount Martha wastewater treatment plant in Victoria, Australia, where dissolved air flotation without polymer dosing is used to thickened sludge. The sludge was stored at 4 °C for 30 days before use to ensure minimal changes due to biological activity during experiments, and to help maintain the stability and consistency between samples (Curvers et al., 2009). To achieve different concentrations, sludge was first
In-situ flow behaviour
As shown in Fig. 1a and b, sludge flow curves varied with treatment duration and temperature. This was true for all concentrations of sludge studied (7–13 wt%). Despite elevated temperatures (80–140 °C), WAS behaviour was best described by the Herschel-Bulkley model:where σ is the shear stress (Pa); σc is the yield stress (Pa); γ̇ is the shear rate (s−1); k is the consistency index (Pa.sn); and n (−) is the flow index.
Sludge exhibited yield stress and shear-thinning behaviour for the
Practical implications
Thermal hydrolysis markedly changes WAS rheology. Compared to untreated sludge, the apparent viscosity and yield stress of thermally treated sludge at 25 °C was 14–72% and 9–60% of their original values, respectively, depending on treatment temperature within the range of 80–140°C. The G’ and G” of treated sludge were also 8–39% and 13–50% their original values, respectively, for the range of temperatures studied. These rheological properties would even further decrease if it was measured in
Conclusion
In-situ characterization of WAS flow behaviour at various concentrations during TH was performed. At all treatment conditions, sludge exhibited non-Newtonian flow behaviour. The impact of treatment temperature, duration of treatment, and sludge concentration on η∞, k, and σc was described by linear, logarithmic, and power-law relationships, respectively. The extent and rate of rheological changes during TH were not affected by increasing sludge concentrations. Thermally-treated WAS exhibited
Declaration of interests
None.
Acknowledgement
The authors would like to thank RMIT University for providing a scholarship to K. Hii, Mt. Martha Wastewater treatment plant for providing sludge samples, and Mr. Navid Moghadam for providing useful discussion.
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