• Title/Summary/Keyword: Underwater discharge plasma

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Remove of Three Pathogenic Bacteria in Cultured Fish and Tetracycline Antibiotics Using Underwater Non-Thermal Dielectric Barrier Discharge Plasma (수중 비열 유전체장벽 방전 플라즈마를 이용한 양식어류의 병원성세균 3종 및 Tetracycline계 항생제 제거)

  • Cho, Kyu Seok;Park, Jong Ho
    • Korean Journal of Fisheries and Aquatic Sciences
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    • v.55 no.6
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    • pp.910-916
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    • 2022
  • The purpose of this study is to evaluate the effect of underwater non-thermal dielectric barrier discharge plasma (DBD plasma) on the sterilization of three types of pathogenic bacteria that cause diseases in freshwater fish and the reduction of a tetracycline antibiotics. This experiment was conducted in the DBD plasma generator, and the voltages used to generate plasma were 11.6 kV and 23.1 kV. The measurement intervals were 0, 1, 5, 10 and 15 min. As a result of DBD plasma treatment, Aeromonas hydrophila, Edwardsiella tarda and Pseudomonas fluorescens were removed 93-99% after 5 min at 23.1 kV, and the tetracycline antibiotics were reduced 70-95% after 15 min at 23.1 kV. In this study, as a result of treating the effluent with DBD plasma at a fish farm where the medicinal bath was conducted with oxytetracycline-HCl (OTC-HCl) products, OTC-HCl decreased by 62% after 10 min at 23.1 kV.

Effect of Graphite Electrode Geometry and Combination on Nanocarbon Synthesis using Underwater Discharge Plasma (수중 방전 플라즈마를 이용한 탄소나노소재 합성 시 흑연전극의 형상과 조합의 영향)

  • Jo, Sung-Il;Lee, Byeong-Joo;Jeong, Goo-Hwan
    • Journal of the Korean institute of surface engineering
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    • v.50 no.2
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    • pp.108-113
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    • 2017
  • We investigated the effect of graphite electrode geometry and combination on nanocarbon material synthesis using underwater discharge plasma(UDP). The UDP system consists of two graphite electrodes and beaker filled with de-ionized water. A high voltage of 15 kV with a frequency of 25 kHz is applied to produce UDP using an alternating-current power source. The UDP system with conical electrodes produced the largest amount of products due to the concentration of electrical fields between electrodes. In addition, hollow-shaped stationary electrode and conical-shaped moving electrode stores discharge-induced bubbles and maintains longer reaction time. We found from Raman spectroscopy and electron microscopy that high quality carbon nanomaterials including carbon nanotubes are synthesized by the UDP system.

Effect of plasma treatment using underwater non-thermal dielectric barrier discharge to remove antibiotics added to fish farm effluent (양식장 배출수에 첨가된 항생제 제거 위한 수중 비열 유전체장벽 방전 플라즈마 처리 효과)

  • Kyu Seok Cho;Han Seung Kang
    • Korean Journal of Environmental Biology
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    • v.40 no.4
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    • pp.641-650
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    • 2022
  • The purpose of this study was to compare the efficiency of air and oxygen injected into the underwater non-thermal dielectric barrier discharge plasma (DBD plasma) device used to remove five types of antibiotics (tetracycline, doxycycline, oxytetracycline, clindamycin, and erythromycin) artificially contained in the fish farm discharge water. The voltage given to generate DBD plasma was 27.8 kV, and the measurement intervals were 0, 0.5, 1, 2, 4, 8, 16 and 32 minutes. Tetracycline antibiotics significantly decreased in 4 minutes when air was injected and were reduced in 30 seconds when oxygen was injected. After the introduction of air and oxygen at 32 minutes, 78.1% and 95.8% of tetracycline were removed, 77.1% and 96.3% of doxycycline were removed, and 77.1% and 95.5% of oxytetracycline were removed, respectively. In air and oxygen, 59.6% and 83.0% of clindamycin and 53.3% and 74.3% of erythromycin were removed, respectively. The two antibiotics showed lower removal efficiency than tetracyclines. In conclusion, fish farm discharge water contains five different types of antibiotics that can be reduced using underwater DBD plasma, and oxygen gas injection outperformed air in terms of removal efficiency.

Decomposition of Aqueous Anatoxin-a Using Underwater Dielectric Barrier Discharge Plasma Created in a Porous Ceramic Tube (다공성 세라믹관내에서 생성되는 수중 유전체 장벽 방전 플라즈마를 이용한 아나톡신-a의 분해)

  • JO, Jin-Oh;Jwa, Eunjin;Mok, Young-Sun
    • Journal of Korean Society of Water and Wastewater
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    • v.30 no.2
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    • pp.167-177
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    • 2016
  • This work investigated the decomposition of aqueous anatoxin-a originated from cyanobacteria using an underwater dielectric barrier discharge plasma system based on a porous ceramic tube and an alternating current (AC) high voltage. Plasmatic gas generated inside the porous ceramic tube was uniformly dispersed in the form of numerous bubbles into the aqueous solution through the micro-pores of the ceramic tube, which allowed an effective contact between the plasmatic gas and the aqueous anatoxin-a solution. Effect of applied voltage, treatment time and the coexistence of nutrients such as $NO_3{^-}$, $H_2PO_4{^-}$ and glucose on the decomposition of anatoxin-a was examined. Chemical analyses of the plasma-treated anatoxin-a solution using liquid chromatography-mass spectrometry (LC-MS) and ion chromatography (IC) were performed to elucidate the mineralization mechanisms. Increasing the voltage improved the anatoxin-a decomposition efficiency due to the increased discharge power, but the energy required to remove a given amount of anatoxin-a was similar, regardless of the voltage. At an applied voltage of 17.2 kV (oxygen flow rate: $1.0L\;min^{-1}$), anatoxin-a at an initial concentration of $1mg\;L^{-1}$ (volume: 0.5 L) was successfully treated within 3 min. The chemical analyses using LC-MS and IC suggested that the intermediates with molecular weights of 123~161 produced by the attack of plasma-induced reactive species on anatoxin-a molecule were further oxidized to stable compounds such as acetic acid, formic acid and oxalic acid.

The Study on the Humic Acid Removal using Underwater Plasma Discharge (수중 방전을 이용한 휴믹산 제거)

  • Hong, Eunjung;Chung, Paulgene;Ryu, Seungmin;Park, Junseuk;Yoo, Seungryul;Lho, Taihyeop
    • Journal of Korean Society on Water Environment
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    • v.28 no.3
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    • pp.367-374
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    • 2012
  • A flotation process has a shorter processing time and needs less space than a sedimentation process. Dissolved air flotation process (DAF) is an efficient flotation method and used in a conventional wastewater treatment process. However, DAF requires the circulation of water containing compressed air and requires expensive installation and operation cost. Plasma Air Flotation (PAF) process is able to float flocs by micro bubbles generated from underwater plasma without the circulation of bubbly water and additional saturators. Therefore, PAF can be an alternative solution overcoming economic barriers. In this study, Humic acid removal efficiency by PAF process was compared with that of sedimentation process. 44.67% and 87.3% reduction rate based on UV 254 absorbance has been measured in sedimentation and PAF respectively. In particular, PAF in the flocculation zone can dramatically remove humic acid from water. In flocculation zone, PAF can separate organic matters but sedimentation cannot.

Characteristics of phenol degradation by using underwater dielectric barrier discharge plasma (수중 유전체 장벽 방전 플라즈마를 이용한 페놀의 분해 특성)

  • Shin, Gwanwoo;Choi, Seungkyu;Kim, Jinsu;Zhu, Qian;Weon, kyoungja;Lee, Sangill
    • Journal of Korean Society of Water and Wastewater
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    • v.33 no.4
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    • pp.243-250
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    • 2019
  • This objective of this study was to investigate the degradation characteristics of phenol, a refractory substance, by using a submerged dielectric barrier discharge (DBD) plasma reactor. To indirectly determine the concentration of active species produced in the DBD plasma, the dissolved ozone was measured. To investigate the phenol degradation characteristics, the phenol and chemical oxygen demand (COD) concentrations were evaluated based on pH and the discharge power. The dissolved ozone was measured based on the air flow rate and power discharged. The highest dissolved ozone concentration was recorded when the injected air flow rate was 5 L/min. At a discharge power of 40W as compared to 70W, the dissolved ozone was approximately 2.7 - 6.5 times higher. In regards to phenol degradation, the final degradation rate was highest at about 74.06%, when the initial pH was 10. At a discharged power of 40W, the rate of phenol decomposition was observed to be approximately 1.25 times higher compared to when the discharged power was 70W. It was established that the phenol degradation reaction was a primary reaction, and when the discharge power was 40W as opposed to 70W, the reaction rate constant(k) was approximately 1.72 times higher.

Decolorization of Azo Dyeing Wastewater Using Underwater Dielectric Barrier Discharge Plasma (수중 유전체장벽방전 플라즈마를 이용한 아조 염색폐수 색도제거)

  • Jo, Jin Oh;Lee, Sang Baek;Mok, Young Sun
    • Applied Chemistry for Engineering
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    • v.24 no.5
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    • pp.544-550
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    • 2013
  • This work investigated the environmental application of an underwater dielectric barrier discharge plasma reactor consisting of a porous hydrophobic ceramic tube to the decolorization of an azo dyeing wastewater. The reactive species generated by the plasma are mostly short-lived, which also need to be transferred to the wastewater right after the formation. Moreover, the gas-liquid interfacial area should be as large as possible to increase the decolorization rate. The arrangement of the present wastewater treatment system capable of immediately dispersing the plasmatic gas as tiny bubbles makes it possible to effectively decolorize the dyeing wastewater alongside consuming less amount of electrical energy. The effect of discharge power, gas flow rate, dissolved anion and initial dye concentration on the decolorization was examined with dry air for the creation of plasma and amaranth as an azo dye. At a gas flow rate of $1.5Lmin^{-1}$, the good contact between the plasmatic gas and the wastewater was achieved, resulting in rapid decolorization. For an initial dye concentration of $40.2{\mu}molL^{-1}$ (volume : 0.8 L; discharge power : 3.37 W), it took about 25 min to attain a decolorization efficiency of above 99%. Besides, the decolorization rate increased with decreasing the initial dye concentration or increasing the discharge power. The presence of chlorine anion appeared to slightly enhance the decolorization rate, whereas the effect of dissolved nitrate anion was negligible.

Disinfection of Escherichia coli and Bacillus subtilis using underwater plasma

  • Yu, Seung-Min;No, Tae-Hyeop;Seok, Dong-Chan;Yu, Seung-Ryeol;Hong, Yong-Cheol;Lee, Bong-Ju
    • Proceedings of the Korean Vacuum Society Conference
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    • 2010.02a
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    • pp.47-47
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    • 2010
  • Discharge under the water is very hard and demand considerable high voltage. But specially improved electrode can generate plasma discharge to salty water with relatively low voltage. A round shape ceramic electrode having many pinholes combined with metallic one can generate plasma. 400 volt, 10 kHz and 3 micro second pulse width were applied to repeatedly running synthetic seawater with 10 L/m velocity, containing cultivated E. coli and Bacillus. As a result, 18, 94, 99.97, 100, 100 % disinfection rates to E. coli and 17.1, 17.1, 82.9, 99.4, 99.9 % disinfection rates to Bacillus subtilis were achieved to 1, 2, 3, 4, 5 times repetitive treatment respectively. In the plasma condition, the ions and electrons are separated and new kinds of components are re-synthesized by the intensive movement of the components. Especially chlorine ions are separated and recombined to residual free chlorine like HOCl, $OCl^-$. The residual free chlorine concentrations of discharged water were 0.25, 0.88, 1.39, 1.59, 1.66 mg $Cl_2$/L after 5 times treatment respectively. Another unconfirmed radical and oxidants for example, OH, $H_2O_2$, and $O_3$ can have an effect on microorganism of course.

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Decomposition of Fe-EDTA in Nuclear Waste Water by using Underwater discharge Plasma

  • Kim, Jin-Kil;Lee, Han-Yong;Kang, Duk-Won;Uhm, Han-Sup
    • Proceedings of the Korean Radioactive Waste Society Conference
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    • 2004.06a
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    • pp.336-336
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    • 2004
  • EDTA contained in decontamination wastes can cause complexation of radioactive captions resulting from its various treatment process such as chemical precipitation, and ion exchange etc. It might also import for elevated teachability and higher mobility of cationic contaminants from conditioned wastes such as waste immobilized in cement or other matrices. Therefore, various cheated or unchlelated EDTAS must be treated to environmentally safe materials.(omitted)

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