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Experimental Research on Development Energy Efficiency of Non-Thermal Plasma Technology

Written By

Tao Zhu

Submitted: April 14th, 2014 Published: April 22nd, 2015

DOI: 10.5772/58881

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1. Introduction

NTP has been recently used to distinguish the one-atmosphere, near room temperature plasma discharges from other plasmas, operating at hundreds or thousands of degrees above ambient. Industrially applied plasma technologies, is that they are 1) non-thermal and 2) operate at or near atmospheric pressure. NTP is a new technology for environmental protection, especially in the field of air pollution control, and has been studied by many researchers for 20 years [1]. Due to NTP generated at normal temperature and atmospheric pressure, easy operation and higher treatment efficiency, compare to the other technologies [2]. So far, NTP technology has been used in many fields and decomposed many kinds of air pollutants. There are many researches focusing on volatile organic compounds (VOCs) decomposition [3], and SO2 and NOx degradations [4,5], and CFCs and odors and mercury treatments [6-8], etc. But during of NTP technology development and application, there is a key problem restricting NTP technology for commercial application [9], that is, how to solve energy consumption [10,11].

In order to resolve this problem, a series of researches were carried out in the world. Platinum based catalyst with NTP generated by a high voltage bipolar pulsed excitation was adopted by some researchers [12]. They found the energy efficiency is 0.14 mol/kWh for 2-Heptanone decomposition when the energy density is 200 J/L, and the energy efficiency decreased to 0.029 mol/kWh using an uncoated monolith when the energy density is 500 J/L. Ogata et al. [13] used NTP reactor packed with BaTiO3 pellets to decompose the aromatics benzene, toluene and o-xylene. The results show BaTiO3 pellets have a function for enhancing electric field strength and improving VOCs decomposition.

In our research, we developed a new ferroelectric packed bed NTP reactor and prepared a sample of Ba0.8Sr0.2Zr0.1Ti0.9O3. Doped some ions (Sr & Zr) into the powder particles and crystal boundary in the experiment, the metal ions such as strontium, zinc and zirconium entered into crystal lattices of BaTiO3 equably and the Curie temperature (Tc) fell [14]. Because of higher permittivity and lower dielectric loss of Ba0.8Sr0.2Zr0.1Ti0.9O3 than those of BaTiO3, Ba0.8Sr0.2Zr0.1Ti0.9O3 shows a better ferroelectric physical property to increase the energy efficiency for VOCs removal.


2. Material and methods

2.1. NTP System

The NTP system consisted of a tube-wire packed-bed reactor system, an AC power supply, a continuous flow gas supplying system and an electric and gaseous analytical system [14]. Dry air (78% N2, 21% O2) was used as a balance gas for toluene decomposition. The whole NTP system refer to reference [14]. The NTP packed-bed reactor was shown in Fig.1. And the schematic diagram of NTP system is shown in Fig.2. As the packed materials in NTP reactors, we selected four packed materials, respectively, including no packed materials, ceramic rings, BaTiO3 rings and Ba0.8Sr0.2Zr0.1Ti0.9O3 rings [14].

Figure 1.

NTP reactor

Reactor: organic-glass tube (i.d.32mm, packed infilling length of packed materials of 200mm); Internal electrode: tungsten filament (i.d.0.5mm); External electrode: dense steel mesh; Packed materials packed in the dark zone, respectively selected ceramic rings, BaTiO3 rings and Ba0.8Sr0.2Zr0.1Ti0.9O3 rings. (after T.Zhu [14])

Figure 2.

Schematic diagram of NTP system for toluene removal 1.air compressor 2.buffer 3.toluene liquid bottle 4.attemperator 5.blender 6.NTP reactor 7.mass flow meter 8.needle valve 9.high voltage 10. oscilloscopes 11.gas chromatograph

2.2. Materials and methods

In the experiment, three kinds of packed materials, including ceramic rings, BaTiO3 rings and Ba0.8Sr0.2Zr0.1Ti0.9O3 rings (hollow cylinder shape, 5 mm i.d., 1 mm wall thick, and 10 mm length), were used to pack into the NTP reactor.

We use the method of water-thermal composite action to prepare a kind of modified ferroelectric of nano-size Ba0.8Sr0.2Zr0.1Ti0.9O3 powder at atmospheric pressure. The prepared detail of nano-Ba0.8Sr0.2Zr0.1Ti0.9O3 refers to our former research [15].

We detected the crystal structures and the surface conditions of the Ba0.8Sr0.2Zr0.1Ti0.9O3 samples by XRD (manufactured by Germany Bruker Co., D8 ADVANCE) and SEM (manufactured by Japan, JEOL-JSM-6500F). We used Micromeritics (manufactured by American Quantachrome Co., NOVA 1000) to determine BET surface area. Using an LCR automatism test instrument (manufactured by China, 4210), we measured the relative permittivity of Ba0.8Sr0.2Zr0.1Ti0.9O3 samples. Toluene analysis was carried out by gas chromatography (manufactured by Aglient Co., HP6890N) with a flame ionization detector (FID). The byproducts were detected by GC-MS (manufactured by American Thermo Finnegan Co.) using EI mode, 70 eV and full scan. Ozone concentration produced in the NTP reactor was measured by an iodine-titration method. The plasma reactor employed an AC power supply of 150 Hz scanning from 0 kV to 100 kV was applied to the reactor in the radial direction. The voltage and current waveforms were measured by oscillograph (manufactured by American Tektronix Co., TDS2014). To investigate the electric characteristics of dielectric barrier discharge (DBD), the voltage applied to the reactor was sampled by a voltage divider with a ratio of 12500:1. Also, the current was determined from the voltage drop across a shunt resistor (R3 =10kΩ) connected in series with the grounded electrode. In order to obtained the total charge and discharge power simultaneously, a capacitor (Cm =2μF) was inserted between the reactor and the ground. The electrical power provided to the discharge was measured using the Q–V Lissajous diagram. Typical Lissajous diagram represents to be a parallelogram, and we could calculate power though calculated the area of parallelogram. The whole methods can be seen in the reference [14].

The removal efficiency, reactor energy density, and energy efficiency of toluene were calculated in the process of NTP as follows [14]:

Toluene removal efficiency (η):


Reactor Input energy density (RED):


Energy efficiency (ζ):


3. Results and discussion

3.1. Detection of modified ferroelectric

The crystal structure of Ba0.8Sr0.2Zr0.1Ti0.9O3 is detected by XRD as shown in Fig.3. From Fig.3, we can think the crystal structure of Ba0.8Sr0.2Zr0.1Ti0.9O3 is a kind of ferroelectric, and very close to BaTiO3 and 59 nm diameter. That means crystal structure of nano-Ba0.8Sr0.2Zr0.1Ti0.9O3 should be a kind of cube crystal structure of calcium-titanium oxide. The BET surface area of Ba0.8Sr0.2Zr0.1Ti0.9O3 are 8.8 m2/g, and Longmuir surface area is 12.3 m2/g or so. The relative permittivity of Ba0.8Sr0.2 Zr0.1Ti0.9O3 is 12000.

Figure 3.

XRD testing results of Ba0.8Sr0.2Zr0.1Ti0.9O3

3.2. Effect of nano-Ba0.8Sr0.2Zr0.1Ti0.9O3 on toluene decomposition

Fig.4 shows the effect of nano-Ba0.8Sr0.2Zr0.1Ti0.9O3 on toluene removal efficiency (toluene: 600 mg/m3; flow velocity: 1 mL/min; dry air) [14]. At the same RED, the removal efficiency of toluene had an order of no packed materials < ceramic rings < BaTiO3 rings < nano-Ba0.8Sr0.2Zr0.1Ti0.9O3 rings. Packed materials in NTP reactor could effectively enhance the energy intensity of input reactor and accelerated toluene decomposition. NTP operating at the RED of 0.76 kJ/L, toluene removal efficiency arrived at 97% and the energy efficiency attained 6.48 g/kWh when the packed materials of Ba0.8Sr0.2Zr0.1Ti0.9O3 are used in NTP reactor [14].

In the electrode gap, if we add the presence of solid material, NTP will be enhance, and homogeneous plasma would be formed rather than a filamentous one. Eliasson et al. [16] found that it is important to pack the packed materials into NTP reactor, and the more high energy electrons properly generated by dielectric barrier discharge (DBD). Due to high energy electrons could destroy the molecular structure of toluene, the removal efficiency is increasing with the numbers of high energy electrons increase.

During the preparation of Ba0.8Sr0.2Zr0.1Ti0.9O3 samples, strontium (Sr) and zirconium (Zr) metal ions can enter crystal lattices of BaTiO3 equably and lower the Curie temperature (Tc) [17]. As a result, the permittivity of Ba0.8Sr0.2Zr0.1Ti0.9O3 is 12000, 8 times higher than that of pure phase of BaTiO3 (1500) in room temperature [15]. According to Yamamoto et al.[18], the permittivity had a significant influence on the discharge energy of NTP reactor.

Figure 4.

Relationship between RED and removal efficiency in four NTP reactors

Fig.5 shows the ozone (O3) concentration with and without the packed materials [14]. O3 concentration is the highest with Ba0.8Sr0.2Zr0.1Ti0.9O3 and is in the order of no packed materials < ceramic rings <BaTiO3 rings < Ba0.8Sr0.2Zr0.1Ti0.9O3 rings at the identical RED.

As a kind of main long-living radicals, O3 was generated and transported to the packed materials to take part in oxidation reaction on the surface of packed materials [14, 19].


In fig.6, we can find O3 concentration increases when REDs change from 0 to 0.7 kJ/L, and the maximum ozone concentration appears at the RED of 7 kJ/L. Yamamoto et al. also found the same change of the pattern of ozone production [20]. Ba0.8Sr0.2Zr0.1Ti0.9O3 has higher relative permittivity than BaTiO3 so that Ba0.8Sr0.2Zr0.1Ti0.9O3 can be electric polarized at normal temperature. Therefore, electric field strength and RED are enhanced significantly [14]. As a result, O3 concentration increases according to Eq.(6) (RED ≤ 0.7 kJ/L). While RED ≥ 0.7 kJ/L, the superfluous high-energy electrons accelerate O3 to transform into O2 according to Eq.(7) and Eq.(8).

Figure 5.

Relationship between RED and ozone concentration in four NTP reactors

Chang et al.[21] found that there are two main mechanisms for VOC decomposition. 1) Directly, electrons attack VOC molecules. 2) indirectly reactions happen between VOC molecules and radicals. And these radicals involve oxygen plasma, free radical groups, ozone, etc. Chang’s results indicate higher O3 concentration is positive to higher removal efficiency. So as packed materials, Ba0.8Sr0.2Zr0.1Ti0.9O3 seems to be better than BaTiO3.

Fig.6 shows the change of energy efficiency (ζ) for toluene removal under the different conditions [14]. The energy efficiency has an order as show as follows at the same RED: no packed materials <ceramic rings <BaTiO3 rings < Ba0.8Sr0.2Zr0.1Ti0.9O3 rings. The energy efficiency is 15 g/kWh with Ba0.8Sr0.2Zr0.1Ti0.9O3 and 11 g/kWh with BaTiO3 at RED of 0.23 kJ/L in the NTP reactor. The results show that Ba0.8Sr0.2Zr0.1Ti0.9O3 has a better ferroelectric property to improve energy efficiency and reduce energy consumption in the NTP process for VOCs control, compared with BaTiO3.

Figure 6.

Relationship between RED and energy efficiency in four NTP reactors

3.3. Byproducts analysis

In the process of toluene abatement, the emission in the outlet was detected by GC-MS at electric field strength of 8 kV/cm in Fig.7 (a). By NIST2000 mass spectrum, the polymerization products formation can be observed, including aldehyde, alcohols, amide, and benzene derivative [22].

In fig.7 (b), the byproducts are very few at electric field strength of 14 kV/cm. We can assume that toluene molecules would be completely oxidized to CO2, CO and H2O in the enough high electric field strength of the enough high input power. In fact, there are a large number of high-energy electrons, ions and free radicals in NTP process. Firstly, eq.(5~8) indicate high-energy electrons take part in reaction with oxygen in air [22]. And at the same time, high-energy electron reacted with H2O and N2 in contaminated air:

e + O22OE8
e + H22H+ OE9
e + H2OH+ H+ eE10
e + 2H2HO2+ 3H+ eE11
e + N2 2N+ eE12

Toluene bond energy between carbon of benzene ring and carbon of substituent radical is 3.6 eV, which is the lowest than that of carbon-carbon bond or hydrocarbon bond. Hydrogen of benzene ring is replaced by methyl, which lead to the stability of benzene ring is broken [14]. So molecule structure of toluene is not stable. In the theoretical point of view, this bond is the most vulnerable and broken. Of course, the other bonds are also likely to be destroyed by high energy electrons. Eq.13 is the possible reaction equations of the process of toluene decomposition [23].

Aldehyde, alcohols, amide, and benzene derivative were form in NTP process during above all of free radical groups reacted with the other reaction fragments. When energy efficiency continuing to increase, the byproducts ought to degraded into CO2, CO and H2O.

Figure 7.

Mass spectrum of byproducts of toluene decomposition


4. Conclusion

In this paper, NTP was generated by DBD at 20℃ and 1 atm. We selected four kinds of packed materials, including no padding, ceramic rings, BaTiO3 rings and Ba0.8Sr0.2Zr0.1Ti0.9O3 rings, which to pack into NTP reactor. Nano-Ba0.8Sr0.2Zr0.1Ti0.9O3 was prepared by the method of water-thermal composite action in our laboratory. By detected, Ba0.8Sr0.2Zr0.1Ti0.9O3 shows better ferroelectric characteristic than BaTiO3. Then this kind of new modified ferroelectric of Ba0.8Sr0.2Zr0.1Ti0.9O3 as the packed materials is used in the packed bed NTP reactor for the first time. During the whole experiments, we attained the best removal efficiency of toluene and the best energy efficiency with Ba0.8Sr0.2Zr0.1Ti0.9O3 rings as packed materials in NTP reactor. For example, toluene removal efficiency arrived at 97% and the energy efficiency stopped at 6.48 g/kWh when RED was 0.76 kJ/L or so, and ozone concentration reached the maximum value when RED was 0.7 kJ/L or so. Ozone concentration is positive to higher removal efficiency. There are aldehyde, alcohols, amide, and benzene derivative, which generated as the byproducts in NTP process and detected by GC-MS. Of course, these byproducts could be decomposed into CO2, CO and H2O entirely at last if we further increased input energy intensity. So nano-Ba0.8Sr0.2Zr0.1Ti0.9O3 as the packed materials in the packed bed NTP reactor would effectively improve energy efficiency for VOCs removal than the other packed materials in NTP reactor.



This work was supported by the National Natural Science Foundation of China (No.51108453), and Program for New Century Excellent Talents in University, and Beijing outstanding talent training project, and the Fundamental Research Funds for the Central Universities (No.2009QH03).


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Written By

Tao Zhu

Submitted: April 14th, 2014 Published: April 22nd, 2015