Crystallization evolution, microstructure and properties of sewage sludge-based glass–ceramics prepared by microwave heating
Highlights
► A reactor is designed to prepare glass–ceramic from sewage sludge by microwave. ► Microwave process has reduced energy consumption for its low reaction temperature. ► Finer and uniform crystals are observed in microwave glass–ceramics. ► Improved properties of microwave glass–ceramics are found. ► We modeled the crystals growth in microwave field.
Introduction
One of the main environmental problems is the safe disposal of the huge amount of sewage sludge that is produced every day in wastewater treatment plants [1]. Among the methods of the treatment of sewage sludge, glass–ceramics preparation seems to be a promising one for converting sewage sludge into novel materials that possess attractive mechanical and chemical properties [2]. Sewage sludge containing large amounts of CaO, SiO2, and Al2O3 can be a good raw material for glass–ceramics production. By controlling the initial composition and by suitable heat treatment, a variety of crystalline phases will be obtained [3]. They exhibit bending strength, Vickers microhardness, fracture toughness, chemical durability and thermal shock resistance superior to those of glass, and in some cases traditional ceramics [4], [5]. It should be noted that the chemical energy of the organic components in sewage sludge could be recovered during the prepared procedure of glass–ceramics as an auxiliary energy source. The chemical energy in sewage sludge can be recovered during the prepared procedure of glass–ceramics as an auxiliary energy source, reducing the emission of CO2 which is favorable to Kyoto Protocol [6]. Other advantages of this technology are the possibility of immobilizing heavy metal ions (held in the framework of glass or encapsulated into the crystallization phase) [7], the large reduction of volume (vary between 40 and 90%), and the flexibility of treatment procedure (which may accept different types of sewage sludge, either municipal or industrial) [8]. Preparing glass–ceramics by the conventional technology is an energy-intensive process, with the process temperature as high as about 1300 °C and the process time required as several hours [9]. Economic analysis of a glass–ceramics preparation system which can process 0.5–1.0 ton of sewage sludge per hour showed that the operating costs of this unit ranged from US$100–420 per ton, including labor, fuel and maintenance [10]. Another critical point in glass–ceramics preparation is the difficulty in controlling the size and the type distributions of the crystals due to the thermal inertia of the conventional heating [11].
To overcome these drawbacks, microwave heating has been developed as an alternative technology for the preparation of dense structural glass–ceramics, which is characterized by shorter reaction time, reduced energy consumption, and suppressed crystal size. It was found that the treatment temperature was decreased from 1300 °C to 1000 °C when a glass–ceramics was sintered from barium aluminosilicate glass in microwave field [12]. It was also reported that an abrasion resistant glass–ceramics was developed from the MgO–Al2O3–TiO2 system in 20 min by microwave heating [13]. Moreover, more uniform and strong bonding was observed in the glass–ceramics prepared by microwave, indicating that microwave energy suppressed the grain growth in crystal phase due to a fast heating rate and apparent low-temperature crystallization [8].
Sewage sludge is a poor receptor of microwave energy to achieve the temperature necessary for preparing glass–ceramics. It has been proved that microwave-induced preparation is possible, if an effective receptor is added into the raw sludge. The temperature of sewage sludge can achieve 1200 °C in microwave field when it was homogeneously blended with microwave receptor, such as graphite and char [9]. However, there are fundamental disadvantages of this method when it is applied in glass–ceramics preparation. The chemical composition of the samples shows uncontrollable changes in virtue of adding microwave receptor, leading to the poor properties of the products. In addition, the microwave receptor could not be recovered due to the encapsulation of silicate matrix in the glass–ceramics, increasing the operating cost of the procedure. Attempts termed as “hybrid microwave sintering” were also made to set around the sample directly to initially heat the material at room temperature [14]. However, the temperature of sewage sludge could not reach high enough owing to the significant reflection loss on the interface between microwave receptor layer and the air surrounding it.
To solve these problems, a new Microwave Melting Reactor (MMR) was designed in this study for preparing glass–ceramics from sewage sludge. In MMR, microwave absorption of sewage sludge can be improved by the double-layer structure and the required temperature can be achieved in a very short of time, usually in a few minutes. A wave-transparent layer was introduced into the MMR system to decrease the reflection coefficient of the interface between the air and the MMR. Another important property of the powder was the low thermal conductivity which could give the sample a good heat insulation quality. The double-layer structure in MMR provides the even distribution of temperature and electromagnetic field in the samples, favoring the production of glass–ceramics with desired qualities. Further researches presented in this paper were focused on: (1) investigating the influence of heat-treatment schedule on the crystallization behavior and microstructure of the microwave-prepared glass–ceramics, (2) defining the evolution of crystallization in microwave field which were hardly found by applying the conventional procedures, and (3) gaining an insight into the chemical and physical properties of the glass–ceramics prepared by microwave in comparison to that obtained from conventional process.
Section snippets
The design of MMR
The 2.45 GHz microwave furnace, which consisted of a rectangular multimode cavity, a continually adjustable power supply (0.50–2.7 kW), a temperature controlling system, and a Microwave Melting Reactor, was used for microwave heating experiment. As shown in Fig. 1, the Microwave Melting Reactor (MMR) consisted of a wave-absorbing layer and a wave-transparent layer. The wave-transparent layer is the surface layer which plays an important role in avoiding the reflection loss of the incident wave on
Thermal analysis of the parent glass
The glass transition temperature (Tg) and crystallization temperature (Tc) of the parent glasses prepared by microwave process and conventional process were determined from the DSC traces as shown in Fig. 5. The DSC profiles from the different processes showed different individual properties with regard to peak position and intensity. For the glass prepared by microwave process, an intense exothermic peak (Tc) was observed at 969.5 °C which was attributed to crystallization from the parent
Conclusion
The presented MMR with double-layer structure was used for preparing glass–ceramics from sewage sludge. Glass–ceramics based on CaO–Al2O3–SiO2 system was developed successfully. Attractive physical and chemical properties of the microwave-processed glass–ceramics were observed, such as higher bending strengths (86.5–93.4 MPa) and lower thermal expansion coefficient (5.29 × 10−6/°C). The leaching tests of heavy metals in the glass–ceramics showed that 950 and 1000 °C samples which contained
Acknowledgements
This study was supported by the National High-tech R&D Program (863 Program) of China (Nos. 2009AA064704 and 2007AA06z348), the National Natural Science Fund of China (No. 50978071) and the State Key Laboratory of Urban Water Resource and Environment, Harbin Institute of Technology (No. 2011TS01).
The authors also appreciate the National Innovation Team Supported by the National Science Foundation of China (No. 50821002).
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2022, Journal of Cleaner ProductionCitation Excerpt :However, the concentrations of all toxic heavy metals in S1–S4 samples are much lower than that in pure SS compared with Table 2, which is mainly the result of dilution through the addition of KE and volatilization of heavy metals, for example, Zn will oxidize violently at high temperature and begin to volatilize above 1000 °C. Therefore, it can be concluded that using SS-based raw materials to prepare ceramics can significantly reduce the concentrations of harmful heavy metals (Tian et al., 2011; Garcia and Valles, 2007), which provides a potential way for the recycling of SS. Fig. 4 depicts the changes of crystalline phase for S1–S4 samples at 1250 °C–1400 °C.