Simultaneous removal of multiple indoor-air pollutants using a combined process of electrostatic precipitation and catalytic decomposition
Graphical abstract
Introduction
Indoor air pollution has been attracting growing attentions. The indoor air pollutants cause serious health risks for residents, especially in the developing countries [1], [2]. In China, half million of premature deaths are caused by indoor air pollution every year [3]. It is urgent to develop novel and effective control method for indoor air pollutions.
Generally, the composition of indoor-air pollutants can be categorized as aerosol and gaseous pollutants. The former mainly includes particulate matter (PM), microorganisms and small droplets in the air [4], [5]; while the latter mainly includes ozone, SO2, CO, volatile organic compounds (VOCs) and semi-volatile organic compounds (SVOCs)[6], [7], [8], [9]. In China, PMs, ozone and VOCs are among the commonly detected and concerning pollutants in indoor air [7], [10]. PMs with small diameters can be breathed deep into human lung. It is worse that PMs often carry contaminants such as organic matters, carbon black, heavy metals and pathogens, bringing heavy concerns with human health risks (for instance exacerbating asthma) [11], [12]. Ozone irritates and damages body tissue, causing allergic or chronicle symptoms [7], [10], [13]. It is also responsible for the formation of indoor secondary organic aerosols. Most VOCs are toxic and the exposure of human in VOCs brings about lots of troubles including poisoning, hormone disruption and cancer [14], [15]. The interaction between ozone and VOCs (especially cigarette smoke) could aggravate the injury on respiratory system [16], [17].
Various technologies have been studied to mitigate the indoor air pollution, including ventilation [18], filtration [5], [11], electrostatic precipitation (ESP) [12], [19], adsorption [20], [21], [22], [23], catalytic oxidation [15], [24], [25], [26], [27] and photo-catalytic oxidation (PCO) [20], [28], [29], [30], [31]. However, more studies are still required to tackle the challenges that have been revealed during researches and applications. On one hand, the mentioned technologies have their own advantages and disadvantages. For instance, filtration and ESP effectively remove aerosols, especially PMs, however, they have limited effect on gaseous pollutants; adsorption and catalytic oxidation eliminate gaseous contaminants, such as VOCs, but they demand periodically replacement of adsorbents or catalysts [32]; PCO could work at room temperature with higher removal efficiency, but there is a risk of secondary pollution formation. Besides, ozone emission has been a major concern for the application of ESP and PCO in indoor environment [33], [34]. Few studies have reported the control of ozone in indoor air. It worth emphasizing that, ESP is promising for aerosol/PM removal without the need of replacing filtering materials; while catalytic oxidation is promising for VOCs removal due to its high efficiency [12], [15], [35]. Shimizu et al. [36] developed a corona reactor and simultaneous removed PMs and HCHO in indoor air. The PMs collection rate was >95%, while the concentration of HCHO was controlled to a level below 0.08 ppm. Vargas’s group [37] synthesized the amorphous TiO2 nanoparticles (NP) using a sol-gel method. The formation mechanism, toxicity and antibacterial properties of the amorphous NPs were investigated. The surface defects were found critical for the toxicity and a “memory effect” to light was also observed [37]. Fang and co-researchers [38] developed a MnOx/SiO2@AC catalyst that can efficiently decompose and utilize ozone, thus removing benzene via ozone-catalytic oxidation at ambient temperatures. Weon et al. [39] modified TiO2 catalyst with Pt and F, enhanced the formation of mobile OH radicals, hindered the deposition of carbonaceous intermediates, improved the stability of catalyst and increased the VOCs removal efficiency. On the other hand, so far, the mentioned technologies mainly focus on the removal of one or two pollutants. Very few studies were on the control of multi-pollutants (especially the complex pollutants in real environment) [40], [41]. For instance, few research works reported the simultaneous control of ozone and cigarette smoke in indoor environment. By contrast, the transformation, interference or competition among different pollutants can be important for indoor air pollutions [36], [42], [43]. It has become a bottle-neck for the further study and potential application of indoor-air purification technologies. Therefore, the simultaneous control of multiple pollutants in indoor air is a key problem to be solved. More researches are still required for the effective combination of several technologies to completely clean the indoor air; while further investigations are also needed to understand the mechanism of simultaneous removal of multi-pollutants.
In this work, a novel process combined with ESP and catalytic decomposition was studied for the simultaneous removal of multiple indoor-air pollutants. The pollutants included PM, real VOCs and ozone, which were either released from a building-material sample or using gaseous mixture. The novel gas-cleaning process can be summarized as: ESP removed PMs, VUV lights generated ozone and initiated UV-catalytic oxidation on the catalysts, while an ozone depleting module (ODM) decomposed the residue ozone. The gas cleaning process using combined technologies was investigated and discussed, while the cleaning performance was evaluated and compared with reported works. The results demonstrated a novel and effective process for improving the indoor air quality (IAQ), while it could also provide a new idea for the decontamination of multi-pollutants in indoor air.
Section snippets
Environmental chamber
A 3 m3 environmental chamber (test chamber) was built according to the Chinese national criteria (GB/T 31107-2014) and was used to evaluate the performance of cleaning process. The test chamber was air-tight and enclosed in a small room built with thermo-isolating planks. Besides, an air-conditioner was installed in the small room to maintain the ambient temperature. The 1.4 m × 1.4 m × 1.5 m chamber was lined with stainless steel to reduce sorption of VOCs on the walls. Injection and sampling
Collection of PMs
Fig. 2 shows the graded number-concentration of PMs in the test chamber during the treatment of multi-pollutant. Cigarette smoke was used as the simulated PM source to investigate the removal of PMs with the presence of multi-pollutants (i.e. VOCs and O3) [43]. Considering the treatment procedure, the UV-catalysis module and ODM were removed in this measurement to give a more accurate results for PM concentrations. PMs were categorized according to their aerodynamic diameters. For instance, PM
Conclusions
A combined process was studied for the removal of indoor air multi-pollutants. Simultaneous and complete removal of particulate matter, formaldehyde, other VOCs and ozone were achieved. Technologies including electrostatic precipitation and catalytic decomposition were integrated. The simultaneous removal of multi-pollutants using the mentioned process was performed in a 3 m3 environmental chamber. Real VOCs released from building material or injected in air flow were both investigated. The
Acknowledgement
The authors gratefully acknowledge the National Natural Science Foundation of China (NSFC) (No. 21677179), Natural Science Foundation of China (NSFC) and the Research Grants Council (RGC) of Hong Kong Joint Research Scheme (No. 51561165015, No.N_HKU718/15), Science and Technology Planning Project of Guangdong Province (2017B050504001) and Special Project for Transforming Scientific and Technological Achievement of Sun Yat-sen University (No. 38000-18843231).
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