Ion generating device for organic matter decomposition treatment and organic matter decomposition treatment device
阅读说明:本技术 有机物分解处理用离子生成装置和有机物分解处理装置 (Ion generating device for organic matter decomposition treatment and organic matter decomposition treatment device ) 是由 中石雅仁 入江纮司 于 2019-01-29 设计创作,主要内容包括:提供一种与以往相比能够使有机物的分解处理能力进一步提高的有机分解处理用离子生成装置和有机物分解处理装置。有机物分解处理用离子生成装置(4)具备:相对配置的针电极(12)和平板电极(13);以及向针电极(12)施加正极性的直流电压的直流电源部(9)。直流电源部(9)具有电压控制部(10),该电压控制部(10)将直流电压设定为预定的电压值,在大气压中使针电极(12)和平板电极(13)之间产生电晕放电。(Provided are an ion generator for organic decomposition treatment and an organic matter decomposition treatment device, which can further improve the decomposition treatment capability of organic matters compared with the conventional one. An ion generation device (4) for organic matter decomposition treatment is provided with: a needle electrode (12) and a plate electrode (13) which are arranged to face each other; and a DC power supply unit (9) for applying a positive DC voltage to the needle electrode (12). The DC power supply unit (9) has a voltage control unit (10), and the voltage control unit (10) sets a DC voltage to a predetermined voltage value and generates corona discharge between the needle electrode (12) and the plate electrode (13) in atmospheric pressure.)
1. An ion generator for decomposing organic substances, which generates ions for decomposing organic substances stored in a storage tank,
the ion generating device for organic matter decomposition treatment is provided with:
a pin electrode and a plate electrode disposed opposite to each other; and
a DC power supply unit for applying a DC voltage of positive polarity to the needle electrode,
the DC power supply unit has a voltage control unit that sets the DC voltage to a predetermined voltage value and generates positive corona discharge between the needle electrode and the plate electrode in atmospheric pressure.
2. The organic matter decomposition treatment ion generating apparatus according to claim 1, comprising a cylindrical electrode supporting member for supporting the needle electrode and the plate electrode,
the electrode support member is configured to dispose the needle electrode and the plate electrode in a hollow space surrounded by a cylindrical inner wall portion so as to face each other, and to generate the positive corona discharge in the hollow space.
3. The ion generating apparatus for organic substance decomposition treatment according to claim 2, comprising a case in which the electrode supporting member is provided,
the housing is provided with an inlet for introducing gas and an outlet for discharging the gas into the storage tank,
the electrode supporting member is disposed such that the discharge port is located on a central axis of the hollow space,
the housing linearly sends the gas introduced from the inlet port to the outlet port through the hollow space.
4. An organic substance decomposition treatment apparatus, wherein the ion generator for organic substance decomposition treatment according to any one of claims 1 to 3 is installed in the storage tank.
Technical Field
The present invention relates to an ion generator for organic matter decomposition treatment and an organic matter decomposition treatment apparatus, and is suitable for use in an organic matter decomposition treatment apparatus for decomposing raw garbage such as vegetable residue.
Background
Conventionally, there is known a raw waste treatment apparatus using active oxygen species for decomposing organic substances such as raw waste (for example, see patent document 1). Patent document 1 discloses, for example, the use of superoxide (O) as an active oxygen species2-), hydroxyl radical (. OH), hydrogen peroxide (H)2O2) Mono oxygen (b), (c), (d) and (d)1O2) Ozone (O)3) And decomposing the raw garbage put into the storage tank.
Such a raw garbage disposal apparatus using active oxygen species has advantages such as being less likely to generate methane gas during decomposition treatment and being capable of suppressing putrefactive odor, as compared with a raw garbage disposal apparatus using bacteria.
Prior art documents
Patent document 1: japanese patent laid-open publication No. 2017-189413
Disclosure of Invention
However, since various organic substances other than raw garbage such as paper may be mixed into raw garbage put into such a raw garbage disposal apparatus, it is desired to develop an organic substance decomposition treatment apparatus having higher decomposition treatment capability than the conventional one in consideration of the trouble of sorting and the like. In addition, from the viewpoint of further shortening the time required for the decomposition treatment, it is also desired to improve the decomposition treatment capability.
Accordingly, an object of the present invention is to provide an ion generating apparatus for organic matter decomposition treatment and an organic matter decomposition treatment apparatus, which can further improve the decomposition treatment ability of organic matter compared to the conventional one.
An ion generating apparatus for organic substance decomposition treatment according to the present invention is an ion generating apparatus for organic substance decomposition treatment that generates ions for decomposing organic substances stored in a storage tank, and includes a needle electrode and a plate electrode that are arranged to face each other, and a dc power supply unit that applies a positive dc voltage to the needle electrode, wherein the dc power supply unit includes a voltage control unit that sets the dc voltage to a predetermined voltage value and generates a positive corona discharge between the needle electrode and the plate electrode in atmospheric pressure.
In the organic matter decomposition treatment apparatus according to the present invention, the ion generator for organic matter decomposition treatment is provided in the storage tank.
According to the present invention, oxonium ions having a high decomposition treatment capability of organic substances can be generated, and therefore, the decomposition treatment capability of organic substances can be further improved by using the oxonium ions as compared with the conventional case.
Drawings
FIG. 1 is a schematic view showing the overall configuration of an organic matter decomposition treatment apparatus according to the present invention.
Fig. 2A is a schematic view showing a structure of an electrode structure, and fig. 2B is a schematic view showing a front structure of the electrode structure.
FIG. 3 is a diagram for explaining electron affinity.
FIG. 4 is a diagram for explaining the evaporation rate v and the heat of vaporization LVA graph of the relationship between.
FIG. 5 is a graph showing the number density of oxonium ions at a position spaced x from the position where oxonium ions are generated.
Fig. 6 is a graph showing measurement results of the evaporation mass of the absorber containing polymer measured for each of the case of irradiating oxonium ions, the case of irradiating negative ions and ozone, the case of irradiating only negative ions, and the case of not irradiating ions and the like.
Fig. 7 is a graph showing measurement results of residual mass of the absorber containing polymer measured for each of the case of irradiating oxonium ions, the case of irradiating negative ions and ozone, the case of irradiating only negative ions, and the case of not irradiating ions and the like.
FIG. 8 is a graph showing the measurement results of the evaporation mass of the polymer-containing absorbent material measured when the polymer-containing absorbent material is irradiated with oxonium ions at a distance of 50cm from the polymer-containing absorbent material and when the polymer-containing absorbent material is not irradiated with ions or the like.
FIG. 9 is a graph showing the measurement results of the residual mass of the polymer-containing absorbent material measured when the polymer-containing absorbent material is irradiated with oxonium ions at a distance of 50cm from the polymer-containing absorbent material and when the polymer-containing absorbent material is not irradiated with ions or the like.
FIG. 10 is a graph showing the measurement results of the evaporation mass of water measured for the case of irradiating oxonium ion and the case of not irradiating ion or the like.
Fig. 11 is a graph showing measurement results of measuring the residual mass of water for each of the case where oxonium ions are irradiated and the case where ions and the like are not irradiated.
Detailed Description
Hereinafter, embodiments of the present invention will be described in detail with reference to the drawings.
< Structure of organic substance decomposition/treatment apparatus of the present invention >
Fig. 1 is a schematic diagram showing the overall configuration of an organic matter decomposition treatment apparatus 1 according to the present invention. The organic matter decomposition treatment apparatus 1 is configured to decompose various organic matters such as raw garbage such as vegetable residues and polymer materials and paper materials by using oxonium ions. Examples of the oxonium ion include hydronium ion, oxatriquinolizine, and triquinolizine oxalate, and the oxonium ion is a positive ion. In this case, the organic matter decomposition treatment apparatus 1 includes a tank 2 for charging organic matter, a blower 3, and an ion generator 4 for organic matter decomposition treatment.
Organic substances to be decomposed are introduced from the inlet 2a of the storage tank 2 and stored in the storage tank 2. The organic matter after the decomposition treatment can be discharged to the outside through the discharge port 2b of the storage tank 2. In this case, the organic substance decomposition treatment apparatus 1 includes a heater and a stirrer, not shown, therein, and heats and stirs the organic substance by irradiating the organic substance in the storage tank 2 with oxonium ions generated in the organic substance decomposition treatment ion generation apparatus 4, thereby evaporating moisture of the organic substance and performing decomposition treatment.
The blower 3 and the organic substance decomposition ion generator 4 are disposed at predetermined positions of the storage tank 2, and the blower 3 and the organic substance decomposition ion generator 4 are connected by a pipe 5. The blower 3 sucks in outside air and sends out the sucked air to the organic substance decomposition treatment ion generator 4 through the pipe 5. The gas sent from the blower 3 into the organic substance decomposition ion generator 4 is sent into the storage tank 2 through the interior of the organic substance decomposition ion generator 4.
The ion generating device 4 for organic matter decomposition treatment includes: a case 8 in which an electrode structure described later is provided; and a dc power supply section 9. The casing 8 is provided with an inlet (not shown) connected to the pipe 5 for introducing the gas discharged from the blower 3 into the casing 8. The casing 8 is provided with a discharge port (not shown) that communicates with the storage tank 2 and discharges the gas from the blower 3 into the storage tank 2.
The casing 8 has a sealed space formed therein, and by introducing the gas from the blower 3 into the sealed space, a gas flow is formed in which the gas flows from the inlet port to the outlet port via an electrode structure (described later). Thereby, the housing 8 sends out the oxonium ions generated inside from the discharge port into the storage tank 2.
The dc power supply unit 9 generates a positive dc voltage and applies the positive dc voltage to the electrode structure in the case 8. The dc power supply unit 9 includes a
< about electrode Structure >
Next, the electrode structure provided in the housing 8 of the organic substance decomposition ion generating device 4 will be described below. As shown in fig. 2A, the
In the present embodiment, the case where the cylindrical
The
More specifically, it is preferable that the
As shown in FIG. 2B, the
As shown in fig. 2B, the
The
In the present embodiment, the case where the support portions 13a of the
The interelectrode distance Y between the needle-like tip 12a of the
Here, as shown in fig. 2A, the
In the case of the structure in which the
Even when the electric field intensity of the DC voltage is 0.25 to 1.5kV/mm, if the voltage value of the DC voltage with positive polarity is less than 5kV, it is difficult to generate sufficient oxonium ions for decomposition treatment of organic substances. Further, when the voltage value of the positive dc voltage exceeds 30kV, the conditions for maintaining the stability of discharge become very strict as compared with the case where the voltage value is 30kV or less, and there is a possibility that the practicability is lowered from the viewpoint of maintenance and the like. Therefore, it is preferable that the electric field strength of the direct current voltage is set to 0.25 to 1.5kV/mm and the voltage value of the direct current voltage having the positive polarity is set to 5 to 30 kV.
As described above, by applying the direct-current voltage of the above-described voltage value to the
The difference between the discharge in vacuum and the discharge in the atmosphere will be described. The
Here, one of the main reactions for generating ions in the discharge space is a generation reaction of molecular ions. For ionizing gas molecules M into molecular ions M+And an electron e-It is necessary to supply the gas molecules M with energy higher than the ionization energy (ionization energy) of the gas molecules M. In the discharge space under atmospheric pressure, this energy is imparted by collision of electrons accelerated in a high-electric-field glow region.
Primary ions generated by the discharge travel in the electric field along the electric line of force in their own polarity. When the primary ions directed toward the
In the case of positive corona discharge in the atmosphere, the oxonium ion becomes a final ion regardless of the discharge condition. The generation and development of oxonium ions in the positive corona discharge in the atmosphere are predicted based on the measured values of the rate constants of the respective basic reactions. Thus, for example, the hydronium ion in the oxonium ion generates N by ionization in the glow region2 +And O2 +As primary ion, via involving mainly H2O is generated by the process of development.
< Oxidation capacity with respect to oxonium ion >
Next, the oxidizing ability of the oxonium ion will be described. The amount of atomic stabilization is the amount of energy released. The electron affinity is energy released when one electron is taken in to the outermost layer. The high electron affinity indicates that the electron is taken from the object and the object itself tends to be stable. That is, it can be said that the oxidation ability is strong when the electron affinity is large.
FIG. 3 is a graph showing the relationship between atomic number and electron affinity. The electron affinity of fluorine (F) and chlorine (Cl), which are halogen elements, is extremely high when compared in the same cycle. The electron affinity of chlorine is very high, 3.617 eV. Usually becomes an anion having a valence of 1 upon ionization. Here, the electron affinity of the 1-valent cation of a certain atom is considered. The 1 st ionization energy of an atom represents the energy required to abstract an electron from the outermost layer of the atom to form a monovalent cation. That is, it can be said that "the electron affinity of a 1-valent cation of a certain atom" is equal to "the 1 st ionization energy of the atom".
The 1 st ionization energy of the rare gas is extremely large in the same period, but it is difficult to ionize the rare gas in, for example, discharge or the like. Except for the rare gas, the elements having ionization energy of 1 st higher than that of hydrogen are only nitrogen, oxygen, fluorine, and chlorine. Fluorine and chlorine are substantially absent as monomers. Nitrogen and oxygen do not become cations having a valence of 1, for example, in discharge. Therefore, the hydrogen ion is largest as the electron affinity of the 1-valent cation.
For example, in the oxonium ion, the hydronium ion is H+And H2O, and thus the electron affinity (oxidizing power) of the hydronium ion is equal to that of the hydrogen ion, about 13.6 eV. From this value, it can be said that the oxidation power of hydronium ions is much higher than the oxidation-reduction potential of active oxygen species.
Next, a verification test for confirming the strength of the oxidizing ability of the oxonium ion was performed. In this verification test, the
In this embodiment, the inter-electrode distance Y120mm, 20kV was applied to the
Then, a plurality of iron nails were prepared, and the opening end portion of the
As a result, in the examples, it was visually confirmed that the entire surface of the iron nail was blackened and rusted. On the other hand, in the comparative example, it was visually confirmed that the surface of the iron nail almost maintained the initial silver color and was hardly rusted. Thus, it was confirmed that the examples have higher oxidizing ability than the comparative examples using active oxygen species.
< relationship between oxidizing power and drying power of oxonium ion >
Here, the boiling point of water was 100 ℃ and the heat of vaporization was 2250 kJ/kg. The boiling point of ethanol is 80.3 ℃, and the gasification heat is 393 kJ/kg. The boiling point of the ether was 34.5 ℃ and the heat of vaporization was 327 kJ/kg. Thus, it is understood that water has an extremely large heat of vaporization. This is thought to be because water molecules have polarity and hydrogen bonds act to form blocks called clusters.
The vaporization heat of water was 2250kJ/kg, which was about 0.4eV per 1 molecule of water. For example, when hydronium ions approach cluster water molecules, the oxidation ability (electron affinity) of 13.6eV acts to strip electrons forming hydrogen bonds, and it is expected that the electrons are converted into free electrons having high energy (about 13 eV). The high-energy free electrons collide with the electrons forming the hydrogen bond, and it is expected that the electrons are further converted into high-energy free electrons.
When the oxonium ion is irradiated, the oxidation reaction is linked, and the size of the cluster molecule is expected to be small. The structure and stability of the water clusters have been studied in recent years through experiments and calculations. In computational chemistry, for cyclic clusters (H)2O)nA structure in which n is 3 to 60 is studied. The calculation results were obtained that the distance between oxygen atoms was shortened as the ring became larger.
This is considered to be because the charge distribution of the molecules that accept hydrogen through hydrogen bonds changes, and the force of supplying hydrogen also increases, so if the aggregate of water becomes large, the hydrogen bonds are synergistically strengthened. This means that if the cluster size becomes small, the heat of vaporization becomes small. Several isomers are expected in the hexamer of water molecules, and it is calculated that cyclic, intrinsic, pocket, cage, and prism substances have approximately the same degree of stability. For the heptamer, 2 kinds of cage isomers were also obtained by calculation, and for the octamer, cyclic isomer and stereoisomer were calculated. Further, as a huge cluster, a fullerene-type 28-mer "bucky water", 280 water molecules were aggregated into a cluster in a regular icosahedron shape, and the minimum value of energy was calculated. In recent years, analysis of water clusters has also been performed by abinitio method (non-empirical method).
Here, if the evaporation rate of water is denoted by v, the vaporization heat is denoted by LVWith respect to these evaporation velocities v and the heat of vaporization LVThe relationship of (a) can be expressed by the Clapeyron-Clausius equation as follows.
v=vO·exp(-LV/kBT)…(1)
Here, vODenotes the integration constant, kBThe Boltzmann constant is shown, and T is temperature.
FIG. 4 shows v/vOValue of as heat of vaporization LVIs expressed as a function of (c). As can be seen from FIG. 4, the heat of vaporization LVWhen smaller, the evaporation rate v becomes larger. Therefore, the oxidation reaction is linked by the irradiation with the oxonium ion, and if the cluster molecule size is small and the vaporization heat is small, the vaporization rate becomes high. Therefore, when the organic material is irradiated with oxonium ions, it is expected that more water is evaporated with the same energy. The test for verifying the drying ability using oxonium ion will be described later in "example".
< action and Effect >
In the above configuration, in the organic decomposition treatment ion generating device 4, the
In this way, in the ion generating apparatus 4 for organic substance decomposition treatment, oxonium ions having high capability of organic substance decomposition treatment can be generated by the positive corona discharge generated between the
In the ion generating apparatus 4 for organic decomposition treatment, the
In the organic decomposition processing ion generating device 4, the
< other embodiments >
The present invention is not limited to the above-described embodiments, and can be modified as appropriate within the scope of the present invention. For example, the
- 上一篇:一种医用注射器针头装配设备
- 下一篇:在轧制扁平轧件时避免磨损边缘