WO2018062222A1 - Method and device for decomposing organic halogen compound - Google Patents
Method and device for decomposing organic halogen compound Download PDFInfo
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- WO2018062222A1 WO2018062222A1 PCT/JP2017/034841 JP2017034841W WO2018062222A1 WO 2018062222 A1 WO2018062222 A1 WO 2018062222A1 JP 2017034841 W JP2017034841 W JP 2017034841W WO 2018062222 A1 WO2018062222 A1 WO 2018062222A1
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- mixing device
- organic halogen
- halogen compound
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- A—HUMAN NECESSITIES
- A62—LIFE-SAVING; FIRE-FIGHTING
- A62D—CHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
- A62D3/00—Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances
- A62D3/10—Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances by subjecting to electric or wave energy or particle or ionizing radiation
- A62D3/11—Electrochemical processes, e.g. electrodialysis
- A62D3/115—Electrolytic degradation or conversion
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- C—CHEMISTRY; METALLURGY
- C07—ORGANIC CHEMISTRY
- C07B—GENERAL METHODS OF ORGANIC CHEMISTRY; APPARATUS THEREFOR
- C07B35/00—Reactions without formation or introduction of functional groups containing hetero atoms, involving a change in the type of bonding between two carbon atoms already directly linked
- C07B35/06—Decomposition, e.g. elimination of halogens, water or hydrogen halides
Definitions
- the present invention relates to a method for decomposing organic halogen compounds, and more particularly, to a method and apparatus for decomposing and removing harmful organic halogen compounds such as difficult-to-decompose PCBs and dioxins.
- Organohalogen compounds have many harmful substances, and in particular, many substances that pollute the environment, such as polychlorinated biphenyls (PCBs), dioxins, and organic pesticides.
- PCBs polychlorinated biphenyls
- dioxins dioxins
- organic pesticides organic pesticides.
- PCB is a hardly decomposable harmful substance, it takes many years for detoxification treatment.
- a metal sodium dispersion oil or an alkali metal organic compound or a Pd / C catalyst is used for hydrogen reduction in the dehalogenation decomposition method. It is difficult to make it 0.5 ppm or less, and the combustion method is mainly used.
- JP2002-756 JP 2001-269673 A JP-A-8-66494 JP 2002-265391 A JP 2002-345991 Republished 2005-092448 (WO2005 / 092448)
- the electrolysis method is characterized in that a hydrogen storage metal or an alloy thereof is used as a cathode, and a method of increasing electrolysis efficiency by using a diaphragm electrolytic layer and an ultrasonic generator and stirring has been proposed. This method is effective for high-concentration PCB, but less effective for low-concentration PCB.
- the present invention is an organic halogen compound decomposition method and apparatus according to the following [1] to [10].
- An organohalogen compound-containing liquid and an alkali metal hydroxide aqueous solution are put into an electrolytic reaction tank and mixed, and a conductive high-speed shearing type miniaturization mixing device such as a disperser or homogenizer is mixed in the mixed liquid.
- the organic halogen compound is one or more selected from organic fluorine compounds, organic chlorine compounds, organic bromine compounds, VOCs, PCBs, dioxins, or organic chlorine-based pesticides [ [1] A method for decomposing an organic halogen compound according to [1].
- the alkali metal hydroxide aqueous solution is one or more selected from a sodium hydroxide aqueous solution, a potassium hydroxide aqueous solution or a lithium hydroxide aqueous solution.
- the high-speed shearing type micronizing / mixing device as a cathode is a conductive high-speed shearing type micronizing / mixing device such as a disperser, a homogenizer, a homomixer, a line mixer, or an emulsion generator [1] ] To [3].
- the method for decomposing an organic halogen compound according to any one of [3].
- An electrolytic reaction tank into which an organic halogen compound-containing liquid and an aqueous alkali metal hydroxide solution are charged, and a conductive high-speed shearing type micronizing / mixing device such as a disperser, line mixer, and homogenizer provided therein
- An organic halogen compound decomposition comprising: a positive electrode disposed in the periphery of the fine mixing device; and a power supply device energized with the fine mixing device as a cathode and the positive electrode as an anode. apparatus.
- the high-speed shearing type micronizing / mixing device as a cathode is a conductive high-speed shearing type micronizing / mixing device such as a disperser, a homogenizer, a homomixer, a line mixer, or an emulsion generator [7] ]
- an organic halogen compound-containing liquid such as PCB or dioxin can be decomposed with high efficiency at normal temperature to 100 ° C. and normal pressure.
- the high-speed shearing type refining / mixing device itself is used as a cathode, and an organic halogen compound such as PCB is refined by high-speed shearing, and at the same time, an alkali metal hydroxide (for example, alkali metal hydroxide generated by electrolysis) By greatly contacting and reacting Na), the reaction rate between the organic halogen compound and the alkali metal can be dramatically increased.
- the present invention adopts an unprecedented idea of causing an electrolytic reaction while using a high-speed shearing-type micronizing / mixing device as a cathode to cause an electrolysis reaction while miniaturizing and mixing. Reacts under normal pressure and can operate safely with only electricity as the power source. Since the decomposition reaction of the present invention is carried out in a large amount of aqueous solution and no dangerous material such as Na metal is used, there is no danger of fire or explosion. Especially for low-concentration PCB-containing liquids, which has been difficult to achieve in the past, the reaction rate is dramatically increased by using the high-speed shearing type micronizing / mixing device as the cathode and making the electrode reaction while miniaturizing. Is done.
- organic chlorine compounds such as PCBs, dioxins, organic pesticides, VOCs, etc.
- organic fluorine compounds organic bromine compounds
- organic bromine compounds which have been difficult to decompose in the past, are also from room temperature to 100 ° C. It became possible to process at normal pressure.
- FIG. 1 It is a schematic diagram of the decomposition apparatus of the organic halogen compound used by a prior art example, (a) A figure is a cross-sectional explanatory drawing, (b) A figure is a top explanatory drawing It is a detailed structure figure of the principal part of the high-speed shearing type
- FIG. 1 is a schematic view of an organohalogen compound decomposition apparatus used in the embodiment of the present invention.
- FIG. 1 (a) is a cross-sectional explanatory view
- FIG. 1 (b) is a top explanatory view.
- 2A and 2B are schematic views of an organic halogen compound decomposition apparatus used in the conventional example.
- FIG. 2A is a cross-sectional explanatory view
- FIG. 2B is a top explanatory view.
- 3 is a detailed structural diagram of the main part of the high-speed shearing type micronizing / mixing device 3, wherein (a) is a front view, (b) is a longitudinal sectional view, and (c) is a bottom view.
- 1 is an electrolytic reaction tank
- 2 is a lid of an electrolytic reaction tank
- 3 is a high-speed shearing type fine-mixing device
- 30 is a cylinder (made of stainless steel)
- 30a is a slit
- 31 is a rotor (made of stainless steel)
- 4 is a motor
- 5 is an anode (insoluble metal electrode)
- 6 is an ultrasonic oscillator
- 7 is a thermometer
- 8 is a base
- 9 is a palladium (Pd) cathode metal plate.
- the solution to be treated next (however, in the case of a solid, it cannot be treated, so it is finely pulverized and made into a colloidal form) is weighed and charged into the electrolytic reaction tank 1, and 2 to 20 times as much water is added.
- Alkali metal hydroxide for example, sodium hydroxide, potassium hydroxide, lithium hydroxide
- 2 to 20 times the halogen element equivalent of the organic halogen compound is added and mixed, and electrolysis is performed using the high-speed shearing type miniaturization mixing device 3 as a cathode.
- the rotational speed of the high-speed rotary shear type refinement mixer is 1,000 to 8,000 RPM, preferably 3,000 to 5,000 RPM, and the distance between the rotor and the stator is 0.5 to 5.0 mm, preferably 1.0. ⁇ 2.0 mm.
- the rotor blades 31a and the slits 30a are not arranged in parallel, and the rotor blades 31a are slightly inclined (around 10 °) (see FIG. 3), that is, the interval S2 is also provided to be inclined non-parallel to the slits 30a. It is preferable for increasing the shearing force for miniaturization and increasing the suction force of the mixed liquid from below. Furthermore, it is also preferable to arrange a separate stirrer in the electrolytic reaction tank 1 to improve the convective mixing of the mixed liquid in the tank.
- FIGS. 3 (a) to 3 (c) The detailed structure of the main part of the high-speed shearing type refinement mixing apparatus 3 is as shown in FIGS. 3 (a) to 3 (c). That is, from a stainless steel cylinder 30 having a large number of slits 30a in the vertical direction, and a rotor 31 provided with a large number of stainless steel long blade-like rotor blades 31a rotatably and radially housed inside thereof. Become. As shown in FIGS. 3B and 3C, a large number of rotor blades 31a extend radially downward from the upper center, and each rotor blade 31a has a small width at the bottom and a large width at the top.
- the mixture that has entered the gap S1 is sheared and refined by high-speed rotation of the rotor blade 31a, and halogen ions (for example, Cl ions) and alkali metal ions (for example, Na ions) in the refined product are frequently generated in the electrolyte.
- an alkali metal halide for example, NaCl
- the mixture of the organic halogen compound-containing material and the alkali metal hydroxide aqueous solution sucked from the lower center of the high-speed shearing type fine mixing device 3 and introduced into the gap S1 is sheared at high speed, It is led out from the slit 30 a and mixed while generating convection in the electrolytic reaction tank 1. At this time, if an ultrasonic wave is applied by the ultrasonic oscillator 6, the efficiency increases.
- the high-speed shearing type refinement mixing apparatus 3 serves as a cathode and is characterized in that an organic halogen compound-containing material, for example, a PCB-containing oil is electrolyzed simultaneously in an alkali metal aqueous solution while being sheared and refined.
- an organic halogen compound-containing material for example, a PCB-containing oil
- the hit ratio at which the Cl of PCB contained in the liquid hits the electrode is remarkably increased, and the electrolysis efficiency is improved.
- the mixing ratio of PCB and water has conventionally required 500 to 1,000 times as much water as emulsion of PCB by electrolysis, but in the present invention, it does not emulsify and electrolyze PCB and water. Since the electrolysis is performed while the PCB is refined by the high-speed shearing type refinement mixing apparatus which is a cathode without using an activator, the ratio of water can be drastically reduced (2 to 20 times). Moreover, since no activator was used, oil / water separation was easy after the reaction, opening the way for industrialization. In addition, the water after oil-water separation can be recycled for the electrolytic treatment of the next PCB.
- the negative electrode rotor 3 (rotating blade 31a) has a high probability of being hit.
- Disposer a high-speed rotary shearing type micronizing and mixing device, was successfully used as a negative electrode. Adopted as a negative electrode.
- the entrance of the high-speed shearing type micronizing / mixing device 3 as shown in FIG. 1 is usually drawn up from below, sheared / miniaturized, and discharged from the top or side.
- the ultrasonic transmitter 6 is installed near (outside) the lower part of the mixing apparatus, it is effective to promote the miniaturization and activation of the PCB.
- the frequency is preferably 20 to 1,000 KHz. (Mixed liquid may be scattered above 1,000KHz)
- Another feature of the present invention is safety. Since it is operated under normal pressure at a low temperature of 100 ° C. or less, the present invention is an electrolysis of PCB using an alkali metal hydroxide aqueous solution as an electrolyte, and does not use dangerous chemicals. Just stop responding and it is completely safe against power outages.
- platinum which is an insoluble metal or an alloy thereof, platinum plating or the like is preferably used.
- a carbon electrode is also suitable.
- the present invention applies to all organic halogen compounds. Although there are considerable harmful compounds in organic fluorine compounds, they are sufficiently treated by this method. Organic bromine compounds can also be treated. It can also be applied to the degradation of pesticides.
- Example 1 20 L of tap water and 100 g of sodium hydroxide were added to 1 L of transformer oil containing 60% (600,000 ppm) of PCB, and electrolysis was performed at 33 ° C. and normal pressure in the electrolytic cell 1 shown in FIG.
- the detailed structure of the main part of the high-speed shearing type micronizing / mixing device 3 is as shown in FIGS. 3 (a) to 3 (c), and a stainless steel cylinder 30 having a large number of slits 30a in the vertical direction;
- the rotor 31 includes a plurality of long blade-like rotor blades 31a that are rotatably and radially housed inside. As shown in FIGS.
- a large number of rotor blades 31a extend radially downward from the upper center, and each rotor blade 31a has a small width at the bottom and a large width at the top. It is a right-angled triangular plate body, and the right-angled portion is arranged close to the upper part inside the cylinder 30.
- the cylinder 3 has an outer diameter of 60 mm, an inner diameter of 54 mm, the slit has a width of 1 mm, and a length of 7 mm, the inner rotor 31 has an outer diameter of 52 mm, and the rotor blade 31a has a thickness of 4 mm.
- the gap S1 between the inner wall surface of the cylinder 30 and the outer wall surface of the rotor blade 31a is 1 mm, and the interval S2 between the rotor blade 31a and the adjacent rotor blade 31a is 3 mm.
- Example 2 20 L of water and 100 g of sodium hydroxide were added to 1 L of transformer oil containing 15% of PCB (150,000 ppm), and electrolysis was initially performed at 48 V, 50 A (constant current) in the electrolytic cell of FIG. The voltage gradually dropped to 27V and 50A after 2 hours. The temperature was 28 ° C. at the beginning, but after 2 hours it reached 90 ° C., so 30 mL of water was added twice and the reaction was completed in 3 hours and 50 minutes. As a result of analysis, PCB was 1,800 ppm, and the removal rate was 98.2%. The rotational speed of the rotor was 5,000 RPM.
- Example 3 Water (20 L) and sodium hydroxide (200 g) were added to 1 kg of a 60% (600,000 ppm) PCB solution obtained by adding 400 g of mineral oil to 600 g of PCB, and electrolysis was performed using the apparatus shown in FIG. Initially, it started with a voltage of 58V and a constant current of 50A, but after 3 hours it became a voltage of 26V and a current of 50A. The temperature was initially 31 ° C. and reached 77 ° C. at the end of 4 hours. After 4 hours, the analysis showed that PCB 600,000 ppm dropped to 7,200 ppm, resulting in a removal rate of 98.8%.
- Example 4 Up to 20 L of water is added to 1 kg of PCB 60% (600,000 ppm) solution obtained by adding 400 g of mineral oil to 600 g of PCB, but 120 g of lithium hydroxide (LiOH) is added instead of sodium hydroxide (corresponding to 200 g of NaOH). Electrolysis was performed using the apparatus shown in FIG. The reaction was almost the same, and the voltage was initially 59 V for a constant current of 50 A, but dropped to 26 V at the end of 4 hours. The temperature started at 28 ° C and reached 80 ° C at the end. As a result of analysis, PCB 600,000 ppm was 6,000 ppm, and the removal rate was 99%. As a result, lithium hydroxide is slightly better, but it seems to have almost the same effect as sodium hydroxide.
- PCB 60% (600,000 ppm) solution obtained by adding 400 g of mineral oil to 600 g of PCB, but 120 g of lithium hydroxide (LiOH) is added instead of sodium hydroxide (corresponding to
- Example 5 110 g of PCB 100% (1,000,000 ppm), 20 L of water, and 200 g of sodium hydroxide were placed in the electrolytic cell of FIG. 1 and electrolyzed at a constant current of 40 A and a voltage of 40 V. Since the PCB was 100% this time, the electrolysis time was doubled to 8 hours. At a constant current of 40A, the voltage dropped from 40V to 20V and finished. The temperature started at 26 ° C and reached 67 ° C at the end. This is probably because the temperature rise of the electrolyte was small because the current was reduced to 40A. As a result of PCB analysis, 1,000,000 ppm was initially reduced to 4,950 ppm, resulting in a removal rate of 99.5%.
- Agricultural chemicals (containing 2.4% dimethylamine (2.4.D) of 2.4 dichlorophenoxy) (500 g), 20 L of water and 200 g of sodium hydroxide were placed in the electrolytic cell shown in FIG. 1, constant current 40 A, initial voltage 42 V was electrolyzed. Since it was the first time for agrochemicals, it was 6 hours in operation. The voltage dropped to the removal and reached 20V, 40A at the end. The temperature started at 26 ° C and ended at 65 ° C. Results of analysis 2.4. D was 0.3% and the removal rate was 99.4%. As a result, it was proved that the present invention is effective for the decomposition of agricultural chemicals and the like.
- Example 7 500 g of PCB, 500 g of mineral oil, 15 L of water, and 200 g of sodium hydroxide were placed in the electrolytic cell of FIG. 1 and electrolyzed at a constant current of 40 A and an initial voltage of 40V.
- the temperature was initially 26 ° C, but increased to 68 ° C. After 4 hours, the voltage dropped to 20 V and the electrolysis process was completed.
- the removal rate was 98.3%.
- the constant current was suppressed to 40 A, the removal rate was somewhat low, but the temperature rise could be avoided.
- PCB 500 g mineral oil 500 g, water 19 L, potassium hydroxide (KOH) 250 g were put in the electrolytic cell of FIG. 1 and were carried out at a constant current of 50 A and a voltage of 50 V (first), but gradually decreased to 20 V.
- the temperature was initially 26 ° C. and 72 ° C. at the end.
- KOH is used instead of NaOH.
- any of NaOH, LiOH, and KOH can be applied to the present invention.
- Example 9 The low-concentration PCB treatment is in a form where the PCB is hidden in the raw material oil, and the hit rate hitting the cathode is extremely reduced, which is a game with time.
- PCB 100 ppm mineral oil
- 20 L of water and 150 g of sodium hydroxide were further added, and electrolysis was performed at a constant current of 50 A and a voltage of 50 V initially. The voltage gradually decreased from 50V to 30V.
- the electrolysis time was analyzed after 10 hours of treatment, the analytical value was 0.8 ppm, which is one step closer to the Japanese standard values of 0 and 5 ppm.
- Example 9 the remaining liquid of Example 9 was further treated for 2 hours under the same conditions for a total of 12 hours.
- the result was set to [Example 9 ′], and the result of analysis was 0.4 ppm (removal rate 99.6%), and the reference value of 0.5 ppm or less could be cleared.
- Table 1 shows a summary of the nine examples and the two conventional examples. Comparing the method of the present invention with the conventional method, the conventional method has a removal rate of about 50% over 8 hours. However, according to the method of the present invention, 98% of the high concentration PCB treatment is 98%. ⁇ 99% treatment was possible. In particular, in the high-speed shearing type refinement mixing device 3, the oil containing PCB or the like is sheared and refined between the gaps S1 while repeatedly hitting the rotor blades 31a. The hit rate of the inclusion hitting the cathode is significantly improved. Moreover, in this-invention Example, it is 2.4. Although D was treated, it can be applied to all decomposition removal of organic halogen compounds.
- Electrolytic reaction tank 2 Electrolytic reaction tank lid 3: High-speed shearing type micronization mixing device 4: Motor 5: Insoluble anode 6: Ultrasonic generator 7: Thermometer 8: Pedestal 9: Pd cathode metal plate 30 : Cylinder 30a: slit 31; rotor 31a; rotor blade S1: gap between the inner wall surface of the cylinder 30 and the outer wall surface of the rotor blade 31a S2: distance between the rotor blade 31a and the adjacent rotor blade 31a
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Abstract
Description
本願発明は、有機ハロゲン化合物の分解方法に係り、特に難分解性のPCBやダイオキシン等の有害有機ハロゲン化合物の分解・除害するための方法及び装置に関する。 The present invention relates to a method for decomposing organic halogen compounds, and more particularly, to a method and apparatus for decomposing and removing harmful organic halogen compounds such as difficult-to-decompose PCBs and dioxins.
有機ハロゲン化合物には有害な物質が多く、特にポリ塩化ビフェニール類(PCB)やダイオキシン類、有機農薬等の環境を汚染する物質が多い。
特にPCBは難分解性有害物なので、無害化処理に長年月を要している現状である。
Organohalogen compounds have many harmful substances, and in particular, many substances that pollute the environment, such as polychlorinated biphenyls (PCBs), dioxins, and organic pesticides.
In particular, since PCB is a hardly decomposable harmful substance, it takes many years for detoxification treatment.
現在PCBを含む廃油の処理について、規制する廃棄物処理法で認められている方法としては、高温熱分解法、脱塩素化分解法、水熱酸化分解法、還元熱化学分解法、光分解法、プラズマ分解法、超臨界法が知られている。
これらの中では特に大型、特殊な装置が必要ではない点、あるいは有害な副生物が生じない点、副生物の再利用が可能となるなどの点から脱塩素化分解法が望ましいと考えられる。
Currently recognized methods for the disposal of waste oil containing PCB include the high-temperature thermal decomposition method, dechlorination decomposition method, hydrothermal oxidation decomposition method, reductive thermal chemical decomposition method, and photolysis method. The plasma decomposition method and the supercritical method are known.
Among these, the dechlorination / decomposition method is considered desirable from the viewpoints that a large-sized and special apparatus is not necessary, that no harmful by-products are generated, and that by-products can be reused.
この様な背景技術で、高濃度の場合は脱ハロゲン分解法の金属ナトリウム分散油やアルカリ金属有機化合物或はPd/C触媒による水素還元が行われており、低濃度PCBについては脱ハロゲン法ではなかなか0.5ppm以下にすることは難しく燃焼法が主体となっている。 In such background technology, in the case of a high concentration, a metal sodium dispersion oil or an alkali metal organic compound or a Pd / C catalyst is used for hydrogen reduction in the dehalogenation decomposition method. It is difficult to make it 0.5 ppm or less, and the combustion method is mainly used.
比較的簡単な操作手段でPCB等を無害化する方法として、PCB等のアルコール溶液に金属カルシウムを添加混合し脱ハロゲン化を行う方法も提案されている。しかしこの方法も有機溶媒を使用しなければならないという問題がある。[特許文献4] As a method for detoxifying PCB and the like by a relatively simple operation means, a method for dehalogenating by adding metallic calcium to an alcohol solution such as PCB and mixing it has also been proposed. However, this method also has a problem that an organic solvent must be used. [Patent Document 4]
またPCBと水又はアセトニトリル等の溶媒を混合し、PCBを電気分解で処理するという方法も提案されている。この方法は比較的簡単にPCBを無害化できる優れた方法であるが、特殊な装置を必要とするという問題がある。[特許文献5] Also proposed is a method in which a PCB is mixed with a solvent such as water or acetonitrile, and the PCB is treated by electrolysis. This method is an excellent method capable of detoxifying PCB relatively easily, but has a problem that a special apparatus is required. [Patent Document 5]
電解法では陰極として水素吸蔵金属又はその合金を用いることを特徴とし、更に隔膜電解層を使い超音波発生機と攪拌により電気分解の効率を上げる方法が提案されている。この方法は高濃度PCBには効果があるが、低濃度PCBでは効果は少ない結果となった。[特許文献6} The electrolysis method is characterized in that a hydrogen storage metal or an alloy thereof is used as a cathode, and a method of increasing electrolysis efficiency by using a diaphragm electrolytic layer and an ultrasonic generator and stirring has been proposed. This method is effective for high-concentration PCB, but less effective for low-concentration PCB. [Patent Document 6]
上記のごとく、従来技術では、常温、常圧で高効率で有機ハロゲン化合物の脱ハロゲン・無害化処理を行うことができなかった。 As described above, according to the conventional technology, it was not possible to dehalogenate / detoxify organic halogen compounds with high efficiency at normal temperature and pressure.
本願発明者は鋭意研究の結果、下記構成発明によって有機ハロゲン化合物含有液を常温から比較的低温(100℃以下)、かつ常圧で高効率で分解することに成功した。
すなわち、本願発明は、下記[1]~[10]記載の有機ハロゲン化合物の分解方法及び装置である。
[1] 電解反応槽内に、有機ハロゲン化合物含有液とアルカリ金属水酸化物水溶液を投入して混合し、また同混合液中にディスパーサー、ホモジナイザー等の導電性の高速剪断型微細化混合装置を浸漬して設け、さらに同微細化混合装置の周辺に陽電極を配設し、前記高速剪断型微細化混合装置を陰極とし、前記陽電極を陽極として通電・電解することを特徴とする有機ハロゲン化合物の分解方法。
[2] 有機ハロゲン化合物が、有機フッ素化合物、有機塩素化合物、有機臭素化合物、VOC類、PCB類、ダイオキシン類又は有機塩素系農薬から選ばれるいずれか1又は2以上であることを特徴とする[1]記載の有機ハロゲン化合物の分解方法。
[3] アルカリ金属水酸化物水溶液が、水酸化ナトリウム水溶液、水酸化カリウム水溶液又は水酸化リチウム水溶液から選ばれる1種又は2種以上であることを特徴とする[1]又は[2] に記載の有機ハロゲン化合物の分解方法。
[4] 陰極とする高速剪断型微細化混合装置が、ディスパーサー、ホモジナイザー、ホモミキサー、ラインミキサー、エマルジョン生成装置等の導電性の高速剪断型微細化混合装置であることを特徴とする[1]~[3]のいずれか1項に記載の有機ハロゲン化合物の分解方法。
[5] 陽電極が、不溶解性金属である白金、イリジウム、オスミニウム等の白金属又はそれらの合金、又はそれらのメッキ製品あるいは炭素であることを特徴とする[1]~[4]のいずれか1項に記載の有機ハロゲン化合物の分解方法。
[6] 電解反応槽内に、超音波振動を付与しながら電解反応を実施することを特徴とする[1]~[5]のいずれか1項に記載の有機ハロゲン化合物の分解方法。
[7] 有機ハロゲン化合物含有液とアルカリ金属水酸化物水溶液が投入される電解反応槽と、その内部に設けられたディスパーサー、ラインミキサー、ホモジナイザー等の導電性の高速剪断型微細化混合装置と、その微細化混合装置の周辺に配設された陽電極と、前記微細化混合装置を陰極とし前記陽電極を陽極として通電する電源装置とから構成されることを特徴とする有機ハロゲン化合物の分解装置。
[8] 陰極とする高速剪断型微細化混合装置が、ディスパーサー、ホモジナイザー、ホモミキサー、ラインミキサー、エマルジョン生成装置等の導電性の高速剪断型微細化混合装置であることを特徴とする[7]に記載の有機ハロゲン化合物の分解装置。
[9] 陽電極が、不溶解性金属である白金、イリジウム、オスミニウム等の白金属又はそれらの合金、又はそれらのメッキ製品あるいは炭素であることを特徴とする[7]又は[8]に記載の有機ハロゲン化合物の分解装置。
[10] 電解反応槽に超音波発振機が付設されてなることを特徴とする[7]~[9]のいずれか1項に記載の有機ハロゲン化合物の分解装置。
As a result of earnest research, the inventor of the present application succeeded in decomposing an organic halogen compound-containing liquid with high efficiency at normal pressure from normal temperature to relatively low temperature (100 ° C. or less) by the following constitutional invention.
That is, the present invention is an organic halogen compound decomposition method and apparatus according to the following [1] to [10].
[1] An organohalogen compound-containing liquid and an alkali metal hydroxide aqueous solution are put into an electrolytic reaction tank and mixed, and a conductive high-speed shearing type miniaturization mixing device such as a disperser or homogenizer is mixed in the mixed liquid. And an anode is disposed around the same fine-mixing device, the high-speed shearing-type fine-mixing device is used as a cathode, and the positive electrode is used as an anode for electrolysis and electrolysis. Method for decomposing halogen compounds.
[2] The organic halogen compound is one or more selected from organic fluorine compounds, organic chlorine compounds, organic bromine compounds, VOCs, PCBs, dioxins, or organic chlorine-based pesticides [ [1] A method for decomposing an organic halogen compound according to [1].
[3] The alkali metal hydroxide aqueous solution is one or more selected from a sodium hydroxide aqueous solution, a potassium hydroxide aqueous solution or a lithium hydroxide aqueous solution. [1] or [2] Of decomposition of organic halogen compounds.
[4] The high-speed shearing type micronizing / mixing device as a cathode is a conductive high-speed shearing type micronizing / mixing device such as a disperser, a homogenizer, a homomixer, a line mixer, or an emulsion generator [1] ] To [3]. The method for decomposing an organic halogen compound according to any one of [3].
[5] Any one of [1] to [4], wherein the positive electrode is a white metal such as platinum, iridium, osmium, or an alloy thereof, or a plated product or carbon thereof, which is an insoluble metal The method for decomposing an organic halogen compound according to
[6] The method for decomposing an organic halogen compound according to any one of [1] to [5], wherein the electrolytic reaction is performed while applying ultrasonic vibration in the electrolytic reaction tank.
[7] An electrolytic reaction tank into which an organic halogen compound-containing liquid and an aqueous alkali metal hydroxide solution are charged, and a conductive high-speed shearing type micronizing / mixing device such as a disperser, line mixer, and homogenizer provided therein An organic halogen compound decomposition comprising: a positive electrode disposed in the periphery of the fine mixing device; and a power supply device energized with the fine mixing device as a cathode and the positive electrode as an anode. apparatus.
[8] The high-speed shearing type micronizing / mixing device as a cathode is a conductive high-speed shearing type micronizing / mixing device such as a disperser, a homogenizer, a homomixer, a line mixer, or an emulsion generator [7] ] The decomposition | disassembly apparatus of the organic halogen compound as described in any one of.
[9] Described in [7] or [8], wherein the positive electrode is a white metal such as platinum, iridium, or osmium which is an insoluble metal, or an alloy thereof, or a plated product or carbon thereof. Organic halogen compound decomposition equipment.
[10] The organohalogen compound decomposition apparatus according to any one of [7] to [9], wherein an ultrasonic oscillator is attached to the electrolytic reaction tank.
本願発明によれば、PCB、ダイオキシン等の有機ハロゲン化合物含有液を常温~100℃以下、かつ常圧で高効率で分解することができる。
本願発明によれば、高速剪断型微細化混合装置そのものを陰極にし、PCB等の有機ハロゲン化合物を高速剪断して微細化すると同時に、それに電解されて生成したアルカリ金属水酸化物のアルカリ金属(例えばNa)を大いに接触・反応させることで、有機ハロゲン化合物とアルカリ金属との反応率を飛躍的上昇させることができる。
本願発明では高速剪断型微細化混合装置を陰極として微細化・混合しながら電解反応を起こさせるという従来にない発想を採用したものであり、反応率も高くなりしかも常温から比較的低温(100℃以下)、常圧のもとで反応し、動力源としては電気のみで、安全操業ができる。
本願発明の分解反応は、大量の水溶液中で行われ、かつNa金属等の危険な材料を使用しないので、火災や爆発等の危険は生じない。
特に従来難しかった低濃度PCB含有液に対しても、高速剪断型微細化混合装置を陰極にして、微細化しながら電極反応させることで反応のヒット率も飛躍的に上がり、PCBが容易に除害される。
そして、本願発明によれば従来分解し難い物質であったPCB類、ダイオキシン類、有機農薬類、VOC類等の有機塩素化合物類、有機フッ素化合物類、有機臭素化合物類も常温~100℃以下、常圧で処理できることとなった。
According to the present invention, an organic halogen compound-containing liquid such as PCB or dioxin can be decomposed with high efficiency at normal temperature to 100 ° C. and normal pressure.
According to the present invention, the high-speed shearing type refining / mixing device itself is used as a cathode, and an organic halogen compound such as PCB is refined by high-speed shearing, and at the same time, an alkali metal hydroxide (for example, alkali metal hydroxide generated by electrolysis) By greatly contacting and reacting Na), the reaction rate between the organic halogen compound and the alkali metal can be dramatically increased.
The present invention adopts an unprecedented idea of causing an electrolytic reaction while using a high-speed shearing-type micronizing / mixing device as a cathode to cause an electrolysis reaction while miniaturizing and mixing. Reacts under normal pressure and can operate safely with only electricity as the power source.
Since the decomposition reaction of the present invention is carried out in a large amount of aqueous solution and no dangerous material such as Na metal is used, there is no danger of fire or explosion.
Especially for low-concentration PCB-containing liquids, which has been difficult to achieve in the past, the reaction rate is dramatically increased by using the high-speed shearing type micronizing / mixing device as the cathode and making the electrode reaction while miniaturizing. Is done.
According to the present invention, organic chlorine compounds such as PCBs, dioxins, organic pesticides, VOCs, etc., organic fluorine compounds, and organic bromine compounds, which have been difficult to decompose in the past, are also from room temperature to 100 ° C. It became possible to process at normal pressure.
本願発明の実施には、まず図1に示すごとき高速剪断型微細化混合装置を備えた有機ハロゲン化合物の分解装置を用意する。
図1は本願発明実施例で用いられる有機ハロゲン化合物の分解装置の概説図であり、(a)図は断面説明図、(b)図は上面説明図である。
なお、図2は従来例で用いられる有機ハロゲン化合物の分解装置の概説図であり、(a)図は断面説明図、(b)図は上面説明図である。
図3は、高速剪断型微細化混合装置3の要部の詳細構造図であり、(a)は正面図、(b)は縦断面図、(c)は底面図である。
図において、1は電解反応槽、2は電解反応槽の蓋、3は高速剪断型微細化混合装置、30は円筒(ステンレススチール製)、30aはスリット、31はロータ(ステンレススチール製)、31aはローター羽根、4はモーター、5は陽極(不溶解性金属電極)、6は超音波発振機、7は温度計、8は台座、9はパラジウム(Pd)陰極金属板である。
次に処理すべき溶液(ただし固体の場合は処理できないので微粉砕してコロイド状とする)を計量して電解反応槽1に投入し、その2~20倍の水を加え、更に処理すべき有機ハロゲン化合物のハロゲン元素当量の2~20倍のアルカリ金属水酸化物(例えば水酸化ナトリウム、水酸化カリウム、水酸化リチウム)を加えて混合し、高速剪断型微細化混合装置3を陰極として電解する。
高速回転剪断型微細化混合装置の回転数は1,000~8,000RPM、好ましくは3,000~5,000RPM、ローターとステーターとの間隔は0.5~5.0mm、好ましくは1.0~2.0mmである。
なお、ローター羽根31aとスリット30aとは平行配列ではなく、ローター羽根31aは若干傾斜(10°前後)して(図3参照)、すなわち間隔S2もスリット30aと非平行に傾斜して設けることが、微細化のための剪断力増大と下方からの混合液の吸引力増強のために好ましい。
さらに、電解反応槽1内に別に攪拌機を配設して、槽内の混合液の対流混合を良好にすることも好ましい。
In carrying out the present invention, first, an organic halogen compound decomposition apparatus equipped with a high-speed shearing type fine-mixing apparatus as shown in FIG. 1 is prepared.
FIG. 1 is a schematic view of an organohalogen compound decomposition apparatus used in the embodiment of the present invention. FIG. 1 (a) is a cross-sectional explanatory view, and FIG. 1 (b) is a top explanatory view.
2A and 2B are schematic views of an organic halogen compound decomposition apparatus used in the conventional example. FIG. 2A is a cross-sectional explanatory view, and FIG. 2B is a top explanatory view.
FIG. 3 is a detailed structural diagram of the main part of the high-speed shearing type micronizing /
In the figure, 1 is an electrolytic reaction tank, 2 is a lid of an electrolytic reaction tank, 3 is a high-speed shearing type fine-mixing device, 30 is a cylinder (made of stainless steel), 30a is a slit, 31 is a rotor (made of stainless steel), 31a Is a rotor blade, 4 is a motor, 5 is an anode (insoluble metal electrode), 6 is an ultrasonic oscillator, 7 is a thermometer, 8 is a base, and 9 is a palladium (Pd) cathode metal plate.
The solution to be treated next (however, in the case of a solid, it cannot be treated, so it is finely pulverized and made into a colloidal form) is weighed and charged into the
The rotational speed of the high-speed rotary shear type refinement mixer is 1,000 to 8,000 RPM, preferably 3,000 to 5,000 RPM, and the distance between the rotor and the stator is 0.5 to 5.0 mm, preferably 1.0. ~ 2.0 mm.
Note that the rotor blades 31a and the slits 30a are not arranged in parallel, and the rotor blades 31a are slightly inclined (around 10 °) (see FIG. 3), that is, the interval S2 is also provided to be inclined non-parallel to the slits 30a. It is preferable for increasing the shearing force for miniaturization and increasing the suction force of the mixed liquid from below.
Furthermore, it is also preferable to arrange a separate stirrer in the
そして、高速剪断型微細化混合装置3の要部の詳細構造は図3(a)~図3(c)に示すごときものである。
すなわち、縦方向に多数のスリット30aを有するステンレススチール製の円筒30と、その内側に回転自在で放射状に内装された多数のステンレススチール製の長羽根状のロ
ータ羽根31aを備えたロータ31とからなる。
図3(b)、(c)に示すごとく、多数のローター羽根31aは、上方中央部から放射状に下方に延設されており、各ローター羽根31aは下方の巾が小さく上方の巾が大きい略直角三角形状の板体であって、直角部が円筒30内部の上部に近接して配置されている。
円筒30内壁面に対向するローター羽根31a外壁面との間には間隙S1があり、多数のローター羽根31aの回転により、有機ハロゲン化合物含有物とアルカリ金属水酸化物水溶液の混合物が下方中央から吸い込まれて間隙S1に導入される。
間隙S1に入った前記混合物は、ローター羽根31aの高速回転によって剪断されて微細化され、微細化物中のハロゲンイオン(例えばClイオン)とアルカリ金属イオン(例えばNaイオン)が電解液中で高頻度で接触して、アルカリ金属ハロゲン化物(例えばNaCl)となって結合して、有機ハロゲン化合物から脱ハロゲンされる。
なお、高速剪断型微細化混合装置3の下方中央から吸い込まれて間隙S1に導入された有機ハロゲン化合物含有物とアルカリ金属水酸化物水溶液の混合物は、高速剪断された後、縦方向の多数のスリット30aから外側へ導出され、電解反応槽1内に対流を生成させながら混合される。
なお、この際に、超音波発振機6により超音波を掛けると効率が上がる。
The detailed structure of the main part of the high-speed shearing type refinement mixing
That is, from a
As shown in FIGS. 3B and 3C, a large number of rotor blades 31a extend radially downward from the upper center, and each rotor blade 31a has a small width at the bottom and a large width at the top. It is a right-angled triangular plate body, and the right-angled portion is arranged close to the upper part inside the
There is a gap S1 between the outer wall surface of the rotor blade 31a facing the inner wall surface of the
The mixture that has entered the gap S1 is sheared and refined by high-speed rotation of the rotor blade 31a, and halogen ions (for example, Cl ions) and alkali metal ions (for example, Na ions) in the refined product are frequently generated in the electrolyte. To form an alkali metal halide (for example, NaCl), which is dehalogenated from the organic halogen compound.
In addition, the mixture of the organic halogen compound-containing material and the alkali metal hydroxide aqueous solution sucked from the lower center of the high-speed shearing type
At this time, if an ultrasonic wave is applied by the
この電解では高速剪断型微細化混合装置3が陰極となっており、アルカリ金属水溶液中で有機ハロゲン化合物含有物、例えばPCB含有油を剪断・微細化しながら同時に電解することが特徴である。
PCB含有油を高速剪断型微細化混合装置3に掛けると、液中に含まれているPCBのClが電極に当たるヒット率が格段に高くなり電解効率が向上する。
PCBが陰電極に触れるか又は近づくとPCB中のClは電子を受けてCl-イオンとなり、PCBから脱離し、生成したCl-イオンは水酸化ナトリウム水溶液中のNa+イオンと結合してNaCl(食塩)となって、PCBが分解する。
In this electrolysis, the high-speed shearing type
When the PCB-containing oil is applied to the high-speed shearing type micronizing /
When the PCB touches or approaches the negative electrode, Cl in the PCB receives electrons to become Cl- ions and desorbs from the PCB, and the generated Cl- ions combine with Na + ions in the aqueous sodium hydroxide solution to form NaCl (salt). ) And PCB is decomposed.
なお、高速剪断型微細化混合装置3の+電極にパラジウム(Pd)をメッキをすると、PCB分解率が向上するので好ましい。
In addition, it is preferable to plate palladium (Pd) on the + electrode of the high-speed shearing type micronizing /
PCBと水の混合比率は、従来PCBをエマルジョン化して電解する方式だったので500~1,000倍の水を必要としていたが、本願発明ではPCBと水をエマルジョン化して電解するのではなく、活性剤を使わず陰極である高速剪断型微細化混合装置によってPCBを微細化しながら電解するので、水の比率を格段に下げる(2~20倍)ことが可能となった。しかも活性剤を使わないので、反応後、油/水の分離が簡単で工業化の道が開けた。
なお、油水分離後の水は次のPCBの電解処理用にリサイクル使用することができる。
The mixing ratio of PCB and water has conventionally required 500 to 1,000 times as much water as emulsion of PCB by electrolysis, but in the present invention, it does not emulsify and electrolyze PCB and water. Since the electrolysis is performed while the PCB is refined by the high-speed shearing type refinement mixing apparatus which is a cathode without using an activator, the ratio of water can be drastically reduced (2 to 20 times). Moreover, since no activator was used, oil / water separation was easy after the reaction, opening the way for industrialization.
In addition, the water after oil-water separation can be recycled for the electrolytic treatment of the next PCB.
高速剪断型微細化混合装置は色々な種類があるが、微細化と同時に電解反応を起こさせる必要があるので、ステンレススチール等の導電性の材料で構成され、PCBが何度も微細化混合装置の陰電極ロータ3(回転刃31a)に当たる確率の多い方が好ましい。
その点で高速回転剪断型微細化混合装置である「ディスパーサー」を陰電極にして良い結果が生まれたが、ホモゲナイザー、ホモミキサー、コロイドミル、ラインミキサー等の高速剪断型微細化混合装置も好適な陰電極として採用される。
There are various types of high-speed shearing type miniaturization mixing equipment, but it is necessary to cause an electrolytic reaction at the same time as miniaturization, so it is made of conductive material such as stainless steel, and PCB is repeatedly miniaturized mixing equipment. It is preferable that the negative electrode rotor 3 (rotating blade 31a) has a high probability of being hit.
In that respect, “Disperser”, a high-speed rotary shearing type micronizing and mixing device, was successfully used as a negative electrode. Adopted as a negative electrode.
微細化を助けるために図1に示すような高速剪断型微細化混合装置3の入り口は、普通は下方から吸い上げて剪断・微細化し上方又は側方から出す方式が多いので、高速剪断型微細化混合装置の下部付近(外側)に超音波発信機6を設置すると、PCBの微細化と活性化を促し有効である。振動数としては20~1,000KHzが好ましい。(1,000KHz以上では混合液が飛散する可能性がある)
In order to assist in miniaturization, the entrance of the high-speed shearing type micronizing /
また本願発明の別の特徴は安全性である。100℃以下の低温で常圧下で稼働されるので、本願発明は電解液にアルカリ金属水酸化物水溶液を使ったPCBの電気分解であって、危険な薬品を使っていないので、電気が止まれば反応が止まるだけで停電に対しても全く安全である。 Another feature of the present invention is safety. Since it is operated under normal pressure at a low temperature of 100 ° C. or less, the present invention is an electrolysis of PCB using an alkali metal hydroxide aqueous solution as an electrolyte, and does not use dangerous chemicals. Just stop responding and it is completely safe against power outages.
陽電極には、不溶性金属である白金又はその合金、白金メッキなどが好適に使用される。炭素電極も好適である。
また本願発明は有機ハロゲン化合物には全て適用される。有機フッ素化合物には有害な化合物がかなりあるが、この方法で充分処理される。
有機臭素化合物も処理できる。また農薬の分解にも適用できる。
For the positive electrode, platinum which is an insoluble metal or an alloy thereof, platinum plating or the like is preferably used. A carbon electrode is also suitable.
The present invention applies to all organic halogen compounds. Although there are considerable harmful compounds in organic fluorine compounds, they are sufficiently treated by this method.
Organic bromine compounds can also be treated. It can also be applied to the degradation of pesticides.
次に、本願発明を実施例に基づいて具体的に説明する。
[実施例1]
PCB60%(600,000ppm)入りのトランス油1Lに水道水20Lと水酸化ナトリウム100gを加え、図1に示す電解槽1で33℃、常圧で電解した。
高速剪断型微細化混合装置3の要部の詳細構造は図3(a)~図3(c)に示すごときものであり、縦方向に多数のスリット30aを有するステンレススチール製の円筒30と、その内側に回転自在で放射状に内装された多数の長羽根状のロータ羽根31aを備えたロータ31とからなる。
図3(b)、(c)に示すごとく、多数のローター羽根31aは、上方中央部から放射状に下方に延設されており、各ローター羽根31aは下方の巾が小さく上方の巾が大きい略直角三角形状の板体であって、直角部が円筒30内部の上部に近接して配置されている。
図において、円筒3は外径60mm、内径54mm、スリットは巾1mm、長さ7mmであり、内部のロータ31の外径は52mmでロータ羽根31aの厚みは4mmである。
そして、円筒30の内壁面とローター羽根31a外壁面との間の間隙S1は1mm、ローター羽根31aと隣接するローター羽根31aの間の間隔S2は3mmである。
Next, the present invention will be specifically described based on examples.
[Example 1]
20 L of tap water and 100 g of sodium hydroxide were added to 1 L of transformer oil containing 60% (600,000 ppm) of PCB, and electrolysis was performed at 33 ° C. and normal pressure in the
The detailed structure of the main part of the high-speed shearing type micronizing /
As shown in FIGS. 3B and 3C, a large number of rotor blades 31a extend radially downward from the upper center, and each rotor blade 31a has a small width at the bottom and a large width at the top. It is a right-angled triangular plate body, and the right-angled portion is arranged close to the upper part inside the
In the figure, the
The gap S1 between the inner wall surface of the
円筒30内壁面に対向するローター羽根31a外壁面との間には間隙S1があり、多数のローター羽根31aの回転により、PCBと水酸化ナトリウム水溶液の混合物が下方中央から吸い込まれて間隙S1に導入される。
間隙S1に入った前記混合物は、ローター羽根31aの高速回転によって剪断されて微細化され、微細化物中のClイオンとNaイオンが電解液中で高頻度で接触して、NaClとなって結合して、PCBから脱塩素される。
なお、高速剪断型微細化混合装置3の下方中央から吸い込まれて間隙S1に導入されたPCB含有物と水酸化ナトリウム水溶液の混合物は、高速剪断された後、縦方向の多数のスリット3aから外側へ導出され、電解反応槽1内に対流を生成させながら混合される。
There is a gap S1 between the outer wall surface of the rotor blades 31a facing the inner wall surface of the
The mixture that has entered the gap S1 is sheared and refined by high-speed rotation of the rotor blades 31a, and Cl ions and Na ions in the refined product come into contact with each other in the electrolyte at a high frequency to be combined as NaCl. And dechlorinated from the PCB.
Note that the mixture of the PCB-containing material and the aqueous sodium hydroxide solution sucked from the lower center of the high-speed shearing type
当初48V、50Aで電解を行ったが、50Aを定電流とした初電圧は次第に下がって2時間後26V、50Aとなった。
ローターの回転数は5,000RPMであった。
Although electrolysis was initially performed at 48V and 50A, the initial voltage with a constant current of 50A gradually decreased to 26V and 50A after 2 hours.
The rotational speed of the rotor was 5,000 RPM.
温度は次第に上がり88℃となった。温度が上がったので2時間後電気を切って冷却した。翌日液温35℃で電解を再開した。再開後初電圧57V、50Aであったが、電圧は徐々に下がり27V、50Aと前日とほぼ同様となった。
通算3時間後水酸化ナトリウム20gを追加投入・混合して、1時間後に電解を終了した。
分析の結果PCB濃度は60%から0.6%(6,000ppm)と1/100に減少し、除去率は99%となった。
The temperature gradually increased to 88 ° C. Since the temperature rose, the electricity was turned off after 2 hours for cooling. The next day, electrolysis was resumed at a liquid temperature of 35 ° C. The initial voltage after resumption was 57V and 50A, but the voltage gradually decreased to 27V and 50A, almost the same as the previous day.
After 3 hours in total, 20 g of sodium hydroxide was additionally charged and mixed, and electrolysis was terminated after 1 hour.
As a result of analysis, the PCB concentration was reduced from 60% to 0.6% (6,000 ppm) to 1/100, and the removal rate was 99%.
[実施例2]
PCB15%(150,000ppm)入りトランス油1Lに水20L、水酸化ナトリウム100gを加え、図1の電解槽で当初48V,50A(定電流)で電解した。電圧は次第に下がり2時間後27V、50Aとなった。
温度は始め28℃であったが2時間後90℃となったので水を30mLづつ2回添加して3時間50分で終了した。分析の結果PCBは1,800ppmとなり除去率98.2%の結果となった。ローターの回転数は5,000RPMであった。
[Example 2]
20 L of water and 100 g of sodium hydroxide were added to 1 L of transformer oil containing 15% of PCB (150,000 ppm), and electrolysis was initially performed at 48 V, 50 A (constant current) in the electrolytic cell of FIG. The voltage gradually dropped to 27V and 50A after 2 hours.
The temperature was 28 ° C. at the beginning, but after 2 hours it reached 90 ° C., so 30 mL of water was added twice and the reaction was completed in 3 hours and 50 minutes. As a result of analysis, PCB was 1,800 ppm, and the removal rate was 98.2%. The rotational speed of the rotor was 5,000 RPM.
[比較例1](従来法1)
高速剪断型微細化混合装置は図2に示すものを使用した。すなわち、陰極でなく単なる高速剪断型微細化混合装置として使い、別途用意したパラジウム金属板を陰極9とし、陽極5は図1と同様に白金メッキチタン板を使って電解を行った。
この方法は従来行ってきた方法で、電解条件はPCB1%(10,000ppm)含有トランス油1L、水20L,水酸化ナトリウム120gの混合液を、49V,50Aで電解したが、電圧は次第に下がり26V,50Aとなった。電解時間は本願実施例の場合の2倍の8時間行った。分析の結果PCB4,700ppmとなり、除去率53%となった。
[Comparative Example 1] (Conventional method 1)
The high-speed shearing type micronizing / mixing apparatus shown in FIG. 2 was used. That is, instead of the cathode, it was used as a simple high-speed shearing type miniaturization mixing apparatus, a separately prepared palladium metal plate was used as the
This method is a conventional method, and the electrolysis conditions were electrolysis of a mixture of 1 L of PCB containing 1% (10,000 ppm) of transformer oil 1 L, water 20 L, and sodium hydroxide 120 g at 49 V and 50 A, but the voltage gradually decreased to 26 V. , 50A. The electrolysis time was 8 hours, which is twice that in the case of the present example. As a result of analysis, PCB was 4,700 ppm, and the removal rate was 53%.
[比較例2](従来法2)
PCB200ppm含むトランス油5L、水20L、水酸化ナトリウム80gを電解槽1内にセットし、電解条件は比較例1とほぼ同様の当初48V、50Aで始めたが、後半26V、50Aと電圧が下がった。8時間後分析の結果PCBは120ppmとなり、除去率40%に留まった。
本願実施例の結果と比べると処理時間を2倍にしたにも拘わらず50%程度の除去率に止まり、本願発明の優位性が証明された。
[Comparative Example 2] (Conventional method 2)
Transformer oil 5 L containing PCB 200 ppm, water 20 L, and sodium hydroxide 80 g were set in the
Compared with the results of the embodiment of the present application, the removal rate is only about 50% despite doubling the processing time, demonstrating the superiority of the present invention.
[実施例3]
PCB600gに鉱油400g加えたPCB60%(600,000ppm)溶液1Kgに水20L、水酸化ナトリウム200gを添加して図1の装置で電解した。
当初電圧58V、電流50A定電流で始めたが、3時間後には電圧26V、電流50Aとなった。温度は当初31℃で4時間終了時には77℃となった。
4時間後終了し分析の結果ではPCB600,000ppmが7,200ppmに下がり、98.8%の除去率となった。
[Example 3]
Water (20 L) and sodium hydroxide (200 g) were added to 1 kg of a 60% (600,000 ppm) PCB solution obtained by adding 400 g of mineral oil to 600 g of PCB, and electrolysis was performed using the apparatus shown in FIG.
Initially, it started with a voltage of 58V and a constant current of 50A, but after 3 hours it became a voltage of 26V and a current of 50A. The temperature was initially 31 ° C. and reached 77 ° C. at the end of 4 hours.
After 4 hours, the analysis showed that PCB 600,000 ppm dropped to 7,200 ppm, resulting in a removal rate of 98.8%.
[実施例4]
PCB600gに鉱油400gを加えたPCB60%(600,000ppm)溶液1Kgに水20Lまでは実施例3と同様であるが、水酸化ナトリウムの代わりに水酸化リチウム(LiOH)120g(NaOH200gに対応)添加して図1の装置で電解した。反応はほぼ同様で定電流50Aに対し電圧は当初59Vであったが、4時間終了時には26Vに下がった。温度は28℃で始まり終了時80℃となった。
分析結果ではPCB600,000ppmが6,000ppmとなり、99%の除去率となった。結果的にはやや水酸化リチウムが良いが、ほぼ水酸化ナトリウムと同様の効果と思われる。
[Example 4]
Up to 20 L of water is added to 1 kg of PCB 60% (600,000 ppm) solution obtained by adding 400 g of mineral oil to 600 g of PCB, but 120 g of lithium hydroxide (LiOH) is added instead of sodium hydroxide (corresponding to 200 g of NaOH). Electrolysis was performed using the apparatus shown in FIG. The reaction was almost the same, and the voltage was initially 59 V for a constant current of 50 A, but dropped to 26 V at the end of 4 hours. The temperature started at 28 ° C and reached 80 ° C at the end.
As a result of analysis, PCB 600,000 ppm was 6,000 ppm, and the removal rate was 99%. As a result, lithium hydroxide is slightly better, but it seems to have almost the same effect as sodium hydroxide.
[実施例5]
PCB100%(1,000,000ppm)110g、水20L、水酸化ナトリウム200gを図1の電解槽に入れ、定電流40A、電圧40Vで電解した。今回はPCB100%なので電解時間を2倍の8時間とした。
定電流40Aで電圧は40Vから20Vに下がり終了した。温度は26℃で始まり、終了時67℃となった。これは電流を40Aに下げたために電解液の温度上昇が少なかった為と思われる。
PCB分析結果では当初1,000,000ppmが4,950ppmに下がり除去率99.5%となった。
[Example 5]
110 g of PCB 100% (1,000,000 ppm), 20 L of water, and 200 g of sodium hydroxide were placed in the electrolytic cell of FIG. 1 and electrolyzed at a constant current of 40 A and a voltage of 40 V. Since the PCB was 100% this time, the electrolysis time was doubled to 8 hours.
At a constant current of 40A, the voltage dropped from 40V to 20V and finished. The temperature started at 26 ° C and reached 67 ° C at the end. This is probably because the temperature rise of the electrolyte was small because the current was reduced to 40A.
As a result of PCB analysis, 1,000,000 ppm was initially reduced to 4,950 ppm, resulting in a removal rate of 99.5%.
[実施例6]
農薬;(2.4ジクロロフェノキシ酢酸ジメチルアミン(2.4.D)49.5%含有物)500g、水20L、水酸化ナトリウム200gを図1の電解槽に入れ、定電流40A,当初電圧42Vで電解した。農薬系は初めてなので6時間操業して終了した。電圧は除除に下がり、終了時20V、40Aとなった。温度は26℃で始まり65℃で終了した。
分析の結果2.4.Dは0.3%となり、除去率は99.4%となった。この結果本願発明は農薬等の分解にも有効であることが実証された。
[Example 6]
Agricultural chemicals: (containing 2.4% dimethylamine (2.4.D) of 2.4 dichlorophenoxy) (500 g), 20 L of water and 200 g of sodium hydroxide were placed in the electrolytic cell shown in FIG. 1, constant current 40 A, initial voltage 42 V Was electrolyzed. Since it was the first time for agrochemicals, it was 6 hours in operation. The voltage dropped to the removal and reached 20V, 40A at the end. The temperature started at 26 ° C and ended at 65 ° C.
Results of analysis 2.4. D was 0.3% and the removal rate was 99.4%. As a result, it was proved that the present invention is effective for the decomposition of agricultural chemicals and the like.
[実施例7]
PCB500g、鉱油500g、水15L,水酸化ナトリウム200gを図1の電解槽に入れ、40A定電流、当初電圧40Vで電解した。温度は当初26℃であったが除除に上昇し、68℃となった。4時間後電圧は20Vに下がり電解処理は終了した。分析の結果8,500ppmとなり、除去率98.3%となった。
本実施例では定電流を40Aに抑えたので、やや除去率が低かったが温度上昇を避けることができた。
[Example 7]
500 g of PCB, 500 g of mineral oil, 15 L of water, and 200 g of sodium hydroxide were placed in the electrolytic cell of FIG. 1 and electrolyzed at a constant current of 40 A and an initial voltage of 40V. The temperature was initially 26 ° C, but increased to 68 ° C. After 4 hours, the voltage dropped to 20 V and the electrolysis process was completed. As a result of the analysis, it was 8,500 ppm, and the removal rate was 98.3%.
In this example, since the constant current was suppressed to 40 A, the removal rate was somewhat low, but the temperature rise could be avoided.
[実施例8]
PCB500g鉱油500g、水19L、水酸化カリウム(KOH)250g、を図1の電解槽に入れ、定電流50A、電圧最初50V(最初)で行ったが、次第に下がり20Vとなった。温度は当初26℃、終了時は72℃となった。4時間反応後分析の結果、当初PCB濃度500,000ppmが4時間後6,000ppmとなり、除去率98.8%となった。
今回はNaOHの代わりにKOHを使った実施例である。この結果NaOH,LiOH,KOH何れも本願発明に適用できることが実証された。
[Example 8]
PCB 500 g mineral oil 500 g, water 19 L, potassium hydroxide (KOH) 250 g were put in the electrolytic cell of FIG. 1 and were carried out at a constant current of 50 A and a voltage of 50 V (first), but gradually decreased to 20 V. The temperature was initially 26 ° C. and 72 ° C. at the end. As a result of the 4-hour post-reaction analysis, the initial PCB concentration of 500,000 ppm became 6,000 ppm after 4 hours, and the removal rate was 98.8%.
In this example, KOH is used instead of NaOH. As a result, it was demonstrated that any of NaOH, LiOH, and KOH can be applied to the present invention.
[実施例9]
低濃度PCBの処理は原料油中にPCBが隠れた形となり、陰極に当たるヒット率が極端に下がるので時間との勝負となる。図1の装置にPCB O.1gと鉱油1,000gを加え(PCB100ppm)、更に水20Lと水酸化ナトリウム150gを添加して定電流50A,電圧は当初50Vで電解した。電圧は徐々に下がり、50Vから30Vになった。電解時間は10時間処理して分析したところ、分析値は0.8ppmとなり、日本の基準値0、5ppmに今1歩の結果となった。
そこで更に実施例9の残液を同じ条件で更に2時間、合計12時間処理した。この結果を[実施例9’]とし分析の結果0.4ppm(除去率99.6%)となり、基準値0.5ppm以下をクリヤーすることができた。
[Example 9]
The low-concentration PCB treatment is in a form where the PCB is hidden in the raw material oil, and the hit rate hitting the cathode is extremely reduced, which is a game with time. In the apparatus of FIG. 1 g and 1,000 g of mineral oil were added (PCB 100 ppm), 20 L of water and 150 g of sodium hydroxide were further added, and electrolysis was performed at a constant current of 50 A and a voltage of 50 V initially. The voltage gradually decreased from 50V to 30V. When the electrolysis time was analyzed after 10 hours of treatment, the analytical value was 0.8 ppm, which is one step closer to the Japanese standard values of 0 and 5 ppm.
Therefore, the remaining liquid of Example 9 was further treated for 2 hours under the same conditions for a total of 12 hours. The result was set to [Example 9 ′], and the result of analysis was 0.4 ppm (removal rate 99.6%), and the reference value of 0.5 ppm or less could be cleared.
以上9例の実施例と2例の従来例の総括を表1に示す。
本願発明の方法と従来法を比較すると、従来の方法では8時間掛けて50%程度の除去率であったが、本願発明の方法によれば高濃度PCBの処理では半分の4時間処理で98~99%の処理ができた。
特に高速剪断型微細化混合装置3ではPCB含有油等が何度もローター羽根31aに当たりながら間隙S1間で剪断され微細化されるので、ローター羽根31aと円筒30を陰極にした本願発明では、PCB含有物の陰極に当たるヒット率が格段に向上する。
また本願発明実施例では、PCB含有物のほか農薬の1例として2.4.Dを処理したが、有機ハロゲン化合物の分解除去には全て適用できる。
Comparing the method of the present invention with the conventional method, the conventional method has a removal rate of about 50% over 8 hours. However, according to the method of the present invention, 98% of the high concentration PCB treatment is 98%. ~ 99% treatment was possible.
In particular, in the high-speed shearing type
Moreover, in this-invention Example, it is 2.4. Although D was treated, it can be applied to all decomposition removal of organic halogen compounds.
1:電解反応槽
2:電解反応槽の蓋
3:高速剪断型微細化混合装置
4:モーター
5:不溶解性陽極
6:超音波発生機
7:温度計
8:台座
9:Pd陰極金属板
30:円筒
30a:スリット
31;ロータ
31a;ローター羽根
S1:円筒30の内壁面とローター羽根31a外壁面との間の間隙
S2:ローター羽根31aと隣接するローター羽根31aの間の間隔
1: Electrolytic reaction tank 2: Electrolytic reaction tank lid 3: High-speed shearing type micronization mixing device 4: Motor 5: Insoluble anode 6: Ultrasonic generator 7: Thermometer 8: Pedestal 9: Pd cathode metal plate 30 : Cylinder 30a: slit 31; rotor 31a; rotor blade S1: gap between the inner wall surface of the
Claims (10)
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| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO2003000395A1 (en) * | 2001-06-25 | 2003-01-03 | Japan Techno Co., Ltd. | Vibratingly stirring apparatus, and device and method for processing using the stirring apparatus |
| JP2004066098A (en) * | 2002-08-06 | 2004-03-04 | Ohbayashi Corp | In situ treatment apparatus and method for volatile organic chlorine compound |
| WO2005092448A1 (en) * | 2004-03-29 | 2005-10-06 | Ait Co., Ltd. | Method and apparatus for dehalogenating organic halide through electrolysis |
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| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| WO2003000395A1 (en) * | 2001-06-25 | 2003-01-03 | Japan Techno Co., Ltd. | Vibratingly stirring apparatus, and device and method for processing using the stirring apparatus |
| JP2004066098A (en) * | 2002-08-06 | 2004-03-04 | Ohbayashi Corp | In situ treatment apparatus and method for volatile organic chlorine compound |
| WO2005092448A1 (en) * | 2004-03-29 | 2005-10-06 | Ait Co., Ltd. | Method and apparatus for dehalogenating organic halide through electrolysis |
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| CN109201214A (en) * | 2018-08-30 | 2019-01-15 | 高福程 | A kind of CEMENTED CARBIDE PRODUCTION manufacture high-efficiency vertical agitating ball mill |
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