JP2002020211A - Plant blight controlling method and apparatus therefor - Google Patents
Plant blight controlling method and apparatus thereforInfo
- Publication number
- JP2002020211A JP2002020211A JP2000198936A JP2000198936A JP2002020211A JP 2002020211 A JP2002020211 A JP 2002020211A JP 2000198936 A JP2000198936 A JP 2000198936A JP 2000198936 A JP2000198936 A JP 2000198936A JP 2002020211 A JP2002020211 A JP 2002020211A
- Authority
- JP
- Japan
- Prior art keywords
- water
- ozone water
- ozone
- plant
- cathode
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
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Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A40/00—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
- Y02A40/10—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
- Y02A40/25—Greenhouse technology, e.g. cooling systems therefor
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/30—Wastewater or sewage treatment systems using renewable energies
- Y02W10/37—Wastewater or sewage treatment systems using renewable energies using solar energy
Landscapes
- Greenhouses (AREA)
- Catching Or Destruction (AREA)
- Water Treatment By Electricity Or Magnetism (AREA)
- Nozzles (AREA)
- Agricultural Chemicals And Associated Chemicals (AREA)
- Electrolytic Production Of Non-Metals, Compounds, Apparatuses Therefor (AREA)
- Cultivation Of Plants (AREA)
Abstract
Description
【0001】[0001]
【発明が属する技術分野】本発明は、オゾン水を用いた
植物の病害防除方法及びその装置に関するものであり、
特に、オゾン分解速度を抑えた持続性のあるオゾン水を
利用して植物の病害防除を行う方法と、これに用いる装
置に関するものである。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method and an apparatus for controlling plant diseases using ozone water.
In particular, the present invention relates to a method for controlling plant diseases using persistent ozone water with a suppressed ozonolysis rate, and an apparatus used for the method.
【0002】[0002]
【従来の技術】オゾンは強い殺菌力を有すると共に速や
かに分解して残留しない性質を有している事から、従来
より、オゾンガスは上水や工業用水の殺菌に利用され、
オゾンを溶解したオゾン水は、食品加工器具や食品表面
の殺菌に使用されている。2. Description of the Related Art Since ozone has a strong bactericidal activity and a property that it is quickly decomposed and does not remain, ozone gas has been used for sterilization of tap water and industrial water.
Ozone water in which ozone is dissolved is used for sterilizing food processing equipment and food surfaces.
【0003】一方、植物の病害防除の目的には、化学合
成農薬を撒布する方法が一般的であるが、近年は、係る
化学合成農薬の撒布は、環境汚染や生物の自然循環シス
テムを破壊する原因となるばかりでなく、農薬を撒布す
る作業者や近くに住む住民の健康にも悪影響があるとし
て敬遠される傾向にあり、特に、市場では「減農薬,無
農薬栽培」の農作物が好感を持って受け入れられてい
る。On the other hand, for the purpose of controlling plant diseases, a method of spraying a chemically synthesized pesticide is generally used. In recent years, however, the spraying of such a chemically synthesized pesticide destroys the environmental pollution and the natural circulation system of living organisms. It is not only a cause, but also tends to be avoided because it has a negative effect on the health of workers spraying pesticides and the residents living nearby. It has been accepted.
【0004】そこで、オゾンの有する強い殺菌力を農業
の分野でも利用する事も種々提案されており、例えば、
食品加工技術Vol.18 No.1(1998)のP
6〜14「オゾン水利用による農産種子および農業用資
材の殺菌」には、種子をオゾン水中に浸漬して殺菌処理
する事により種子伝染性病害の発病が抑止される事が報
告されており、又、特開平8−103176号公報に
は、人体に対して無害な低濃度のオゾン水を、育成中の
野菜や果物、或いは収穫後の野菜や果物にオゾン水を撒
布して病害虫の駆除と殺菌を行う方法が開示されてい
る。Therefore, various proposals have been made to utilize the strong sterilizing power of ozone also in the field of agriculture.
Food Processing Technology Vol. 18 No. 1 (1998) P
6-14 "Sterilization of agricultural seeds and agricultural materials by using ozone water" reports that seeds are immersed in ozone water and sterilized to prevent the transmission of seed-borne diseases. Japanese Patent Application Laid-Open No. 8-103176 discloses that low-concentration ozone water harmless to the human body is sprayed on growing vegetables and fruits, or on harvested vegetables and fruits to control pests and insects. A method for performing sterilization is disclosed.
【0005】[0005]
【発明が解決しようとする課題】係る従来の方法におい
て、先ず、化学合成農薬を用いるものは、周知の通り、
残留農薬による土壌や環境の汚染等の種々の問題が提起
されており、世論は減農薬,無農薬の方向に向いている
が、それらを可能とする有効な代替技術がなく、又、単
に化学合成農薬の使用を中止するだけの減農薬,無農薬
栽培では、収穫物の外観や収穫量減少等の問題が伴って
いる。In such conventional methods, first, those using a chemically synthesized pesticide are well known,
Various problems such as soil and environmental pollution due to pesticide residues have been raised, and public opinion has been directed toward reduced pesticides and pesticide-free, but there is no effective alternative technology that makes them possible. In pesticide-reduced and pesticide-free cultivation that only stops using synthetic pesticides, there are problems such as the appearance of the crop and a decrease in the yield.
【0006】一方、オゾン水を用いる方法は、オゾンの
強い殺菌能を利用するものであるが極めて短時間で分解
するため、その効力持続期間に問題がある。又、前記特
開平8−103176号公報では、オゾンガスを生成さ
せ、これを水に溶解させて人体に影響のない程度の低濃
度オゾン水(MITのAsburyは、マサチューセッ
ツ州のMetropolitan District
Commissionの委託による調査結果として、
0.05ppm以下は問題ないとしている。)を撒布す
るものであり、実効は期待し難い。特に、従来の殺虫剤
に代えて係る低濃度オゾン水で病害虫を駆除するとの記
載は、実現性に疑問がある。[0006] On the other hand, the method using ozone water utilizes the strong sterilizing ability of ozone, but decomposes in an extremely short time, and thus has a problem in its effective duration. In Japanese Patent Application Laid-Open No. 8-103176, ozone gas is generated and dissolved in water so as to have a low-concentration ozone water that does not affect the human body (MIT's Asbury is manufactured by Metropolitan District, Mass., USA).
As a result of a commission commissioned by Commission,
It is said that 0.05 ppm or less is not a problem. ), And its effectiveness is unlikely to be expected. In particular, the statement that pests are controlled with low-concentration ozone water in place of conventional pesticides is questionable about its feasibility.
【0007】本発明は、係る従来の問題点に鑑みてなさ
れたもので、オゾン水による実効性のある植物の病害防
除方法と、これに使用する装置を提供する事を目的とす
るものである。The present invention has been made in view of the above-mentioned conventional problems, and has as its object to provide an effective method for controlling plant diseases using ozone water and an apparatus used for the method. .
【0008】[0008]
【課題を解決するための手段】本発明の植物の病害防除
方法は、係る観点の元になされたものであって、第一の
特徴は、オゾン濃度を30ppm以下、好ましくは2〜
20ppmの比較的高濃度オゾン水を、植物の地上部に
撒布する点にあり、これにより、植物体表面に付着した
病原菌を強力に殺菌すると共に、オゾン水から気化した
オゾンガスによる植物体表面近傍における有効オゾンガ
ス濃度を高くして、植物の体表面近傍の病原菌をも殺菌
して植物の病害を防除するものである。Means for Solving the Problems The method for controlling plant diseases of the present invention has been made based on such a viewpoint. The first characteristic is that the ozone concentration is 30 ppm or less, preferably 2 to 30 ppm.
A relatively high concentration of ozone water of 20 ppm is sprayed on the aerial part of the plant, thereby strongly disinfecting the pathogenic bacteria attached to the surface of the plant and the vicinity of the surface of the plant by ozone gas vaporized from the ozone water. By increasing the effective ozone gas concentration, pathogens near the plant body surface are also killed to control plant diseases.
【0009】第二の特徴は、前記オゾン水を弱酸性水と
なすものであり、これにより、貯留中及び配管内輸送中
におけるオゾン水中のオゾンの分解速度を抑えてオゾン
の効果持続時間を長くし、オゾン水撒布の実効を高める
点にある。この場合のオゾン水のpHは、3以上且つ7
未満が好ましく、pH調整は、酸を添加して行う方法が
一般的であり、この場合に使用する酸としては、植物の
成育中は希塩酸,希硫酸等の強酸の希釈水溶液を用いる
ことができ、可食部である野菜や果実の収穫前には、酢
酸,クエン酸,リンゴ酸等の弱酸を添加して前記pH調
整を行うのが好ましい。[0009] The second feature is that the ozone water is made into a weakly acidic water, whereby the rate of decomposition of ozone in the ozone water during storage and transportation during piping is suppressed, and the duration of the ozone effect is extended. In addition, the point is to enhance the effectiveness of ozone water spraying. In this case, the pH of the ozone water is 3 or more and 7
It is generally preferable to adjust the pH by adding an acid. In this case, a dilute aqueous solution of a strong acid such as dilute hydrochloric acid or dilute sulfuric acid can be used during the growth of the plant. Before harvesting the edible portion of vegetables and fruits, it is preferable to adjust the pH by adding a weak acid such as acetic acid, citric acid, malic acid or the like.
【0010】オゾン水としては、高濃度オゾン水が得易
い水の電気分解法により陽極側に生成させたオゾン水が
好ましい。この場合に、電解のための原料水として、ア
ルカリ金属型イオン交換樹脂を用いて軟水化処理した軟
水を使用した場合には、陰極側にアルカリ水が生成する
ので、このアルカリ水を、灌水として前記植物の根元又
はその近傍に撒布する事もできる。これにより、植物の
生理機能の強化と共に該植物の根元やその近傍の地表面
に落下した前記弱酸性のオゾン水を中和してオゾン水中
のオゾンの分解を促進させる効果もある。As the ozone water, ozone water generated on the anode side by electrolysis of water in which high-concentration ozone water is easily obtained is preferable. In this case, when water softened using an alkali metal-type ion exchange resin is used as raw water for electrolysis, alkaline water is generated on the cathode side. It can be sprayed on the root of the plant or in the vicinity thereof. This has the effect of strengthening the physiological function of the plant and neutralizing the weakly acidic ozone water that has fallen to the root of the plant or in the vicinity of the ground surface, thereby promoting the decomposition of ozone in the ozone water.
【0011】更に、上記植物の病害防除方法を実施する
ための好ましい装置としては、水の電気分解法によって
陽極側にオゾン水を生成するオゾン水製造装置における
オゾンを排出する陽極側排水管には、植物の地上部にオ
ゾン水を撒布するための撒布ノズルを有するオゾン水撒
布配管を接続し、一方、陰極側排水管には、前記植物の
根元部又はその近傍に陰極水を撒布するための撒布ノズ
ルを有する陰極水撒布配管を接続したものを基本とし、
この変形例としては、前記オゾン水をオゾン水タンクに
貯蔵し、該タンクからポンプを経て前記オゾン水撒布配
管にオゾン水を供給する様にしたものがあり、この場合
のオゾン水タンクは、オゾン水の自然分解速度を抑制す
る観点から、密閉構造のタンクであるのが好ましい。Further, as a preferable apparatus for carrying out the above-mentioned method for controlling plant diseases, an anode-side drain pipe for discharging ozone in an ozone water producing apparatus which generates ozone water on the anode side by a water electrolysis method is provided. Connecting an ozone water spraying pipe having a spray nozzle for spraying ozone water on the above-ground part of the plant, while connecting the cathode-side drainage pipe with the cathode water at the root of the plant or in the vicinity thereof. Based on the connection of the cathode water spray pipe with a spray nozzle,
As a modified example, there is one in which the ozone water is stored in an ozone water tank, and the ozone water is supplied from the tank to the ozone water distribution pipe via a pump. From the viewpoint of suppressing the spontaneous decomposition rate of water, a tank having a closed structure is preferable.
【0012】又、前記電解式オゾン水製造装置に供給す
る原料水をアルカリ金属型イオン交換樹脂を用いて軟水
化処理する軟水化装置を配置するのが好ましく、この場
合には、前記電解式オゾン水製造装置の陰極側にはアル
カリ水を生成するので、前記陰極水撒布配管からアルカ
リ水を撒布する様になし、更に、該アルカリ水を一旦ア
ルカリ水タンクで貯蔵した後、ポンプを介して前記陰極
水撒布配管からアルカリ水を撒布する様になしている。It is preferable to provide a water softening device for softening raw water supplied to the electrolytic ozone water producing device by using an alkali metal ion exchange resin. Since the alkaline water is generated on the cathode side of the water producing apparatus, the alkaline water is sprayed from the cathode water spray pipe, and the alkaline water is once stored in an alkaline water tank, and then the alkaline water is pumped through a pump. Alkaline water is sprayed from the cathode water spray pipe.
【0013】又、上記装置を可搬式にしたものとして、
原料水タンク,電解式オゾン水製造装置及び該電解式オ
ゾン水製造装置を稼働させるための発電装置とを車両に
搭載して、広大な果樹園等にも適用可能にしたものもあ
る。[0013] Further, the above device is made portable,
There is also a vehicle in which a raw water tank, an electrolytic ozone water producing device, and a power generating device for operating the electrolytic ozone water producing device are mounted on a vehicle to be applicable to a vast orchard or the like.
【0014】[0014]
【発明の実施の形態】以下、本発明について詳細に説明
する。図1は、本発明に係る植物の病害防除方法を実施
するための装置の一例を示す概念図であり、オゾン水製
造装置1としては、水の電気分解方式によるオゾン水製
造装置を用いた場合の例である。同図において、水道水
等の適宜の原水を配管10からバルブV1を経て軟質化
装置11に供給し、ここで軟水化処理された原料水を、
前記電解式オゾン水製造装置1に供給する。該装置1内
では、陽極側に供給された原料水は、陽極側排水管5か
らオゾン水として排出され、バルブV2を経てオゾン水
撒布配管5aに送給される。同様に陰極側に供給された
原料水は、陰極側排水管6から陰極水としてバルブV3
を経て陰極水撒布配管6aに送給される。BEST MODE FOR CARRYING OUT THE INVENTION Hereinafter, the present invention will be described in detail. FIG. 1 is a conceptual diagram showing an example of an apparatus for carrying out the method for controlling plant diseases according to the present invention. In the case where an ozone water producing apparatus using a water electrolysis method is used as an ozone water producing apparatus 1. This is an example. In the figure, an appropriate raw water such as tap water is supplied from a pipe 10 to a softening device 11 via a valve V1, and the raw water subjected to the softening treatment is
It is supplied to the electrolytic ozone water producing apparatus 1. In the apparatus 1, the raw water supplied to the anode side is discharged as ozone water from the anode side drain pipe 5, and is supplied to the ozone water spray pipe 5a via the valve V2. Similarly, the raw water supplied to the cathode side is supplied from the cathode side drain pipe 6 as cathode water to the valve V3.
Is supplied to the cathode water spray pipe 6a.
【0015】ここで上記電解式オゾン水製造装置1につ
いて説明すると、同装置は、特開平8−134677号
等に示されている公知の装置であって、図3にその概要
を示している。即ち、耐オゾン性のフッ素系イオン交換
膜等の有機物固体電解質膜21の一方の面に、オゾン発
生触媒機能を有する貴金属製の金網等からなる陽極電極
22を該電解質膜21に重ね合わせる様にして配置し、
他方の面には、同様に陰極電極23を該電解質膜に重ね
合わせる様にして配置すると共に、両電極の外側面に
は、夫々チタン或いはステンレス鋼等のオゾン耐蝕性を
有する金属製のラス網24,25が全長に亘って配置さ
れており、両電極間に直流電圧を印加できる様に、各電
極は直流電源(図示せず)に接続されている。又、各電
極22,23とラス網24,25とを内包する様に、外
側に陽極側ジャケット20と陰極側ジャケット30が夫
々配置され、各ジャケットには、陽極側原料水流入口2
6,陰極側原料水流入口27及び陽極水(オゾン水)排
出口28,陰極水排出口29が夫々設けられている。Now, the electrolytic ozone water producing apparatus 1 will be described. The apparatus is a known apparatus disclosed in Japanese Patent Application Laid-Open No. 8-134677 and the like, and its outline is shown in FIG. That is, an anode electrode 22 made of a noble metal wire mesh having an ozone generation catalytic function is overlapped on the electrolyte membrane 21 on one surface of an organic solid electrolyte membrane 21 such as an ozone-resistant fluorine-based ion exchange membrane. Place
On the other surface, a cathode electrode 23 is similarly arranged so as to be superimposed on the electrolyte membrane, and on the outer surfaces of both electrodes, a metal mesh made of titanium or stainless steel or the like having ozone corrosion resistance is used. 24 and 25 are arranged over the entire length, and each electrode is connected to a DC power supply (not shown) so that a DC voltage can be applied between both electrodes. Further, an anode-side jacket 20 and a cathode-side jacket 30 are arranged on the outside so as to include the electrodes 22 and 23 and the lath nets 24 and 25, respectively.
6, a cathode side raw material water inlet 27, an anode water (ozone water) outlet 28, and a cathode water outlet 29 are provided respectively.
【0016】係る装置において、両電極間に直流電圧を
印加すると共に原料給水管10からバルブV1a,V1
bを経て前記各原料水流入口26,27に原料水を供給
しつつ電解を行うと、陽極22側には水の電解により生
成したOHイオン(OH- )が集まり、このOHイオン
は、陽極のオゾン発生触媒の作用によってオゾンが発生
すると共に、直ちに水中に溶解してオゾン水が生成す
る。このオゾン水は、陽極水(オゾン水)排出口28か
ら前述の陽極水排出管5を経てオゾン水撒布配管5aに
送給される。ここで、陽極電極22の外面近傍には、千
鳥状に金網が互いに接合されているラス網24によって
複雑に入り組んだ流路が形成されているので、陽極電極
外面には多数の小さな渦流が生じ、この結果、電極面で
発生したオゾンは渦流に巻き込まれて速やかに水中に溶
解するので、オゾンガスとして水流と共に流出するオゾ
ン量は減少し、即ち、溶解オゾン量が増加して30pp
m程度の高濃度オゾン水が得られる事になる。In such an apparatus, a DC voltage is applied between both electrodes, and the valves V1a, V1
When the electrolysis is performed while the raw water is supplied to the raw water inlets 26 and 27 via b, OH ions (OH − ) generated by the electrolysis of the water are collected on the anode 22 side, and the OH ions are supplied to the anode. Ozone is generated by the action of the ozone generating catalyst, and is immediately dissolved in water to generate ozone water. The ozone water is supplied from the anode water (ozone water) outlet 28 to the ozone water spray pipe 5a through the above-described anode water discharge pipe 5. Here, in the vicinity of the outer surface of the anode electrode 22, since a complicated and complicated flow path is formed by the lath net 24 in which the wire nets are joined in a staggered manner, a large number of small eddies are generated on the outer surface of the anode electrode. As a result, the ozone generated on the electrode surface is entrained in the vortex and rapidly dissolved in water, so that the amount of ozone flowing out with the water stream as ozone gas decreases, that is, the amount of dissolved ozone increases to 30 pp.
Thus, ozone water having a high concentration of about m can be obtained.
【0017】尚、前記陽極側原料水流入口26又はオゾ
ン水排出口28のいずれかの近傍に前記微量の酸を添加
可能となす事により、オゾン水のpHを弱酸性に調整す
る事も可能であり、特に前記陽極側原料水流入口26内
に添加しておけば、原料水の電気電導度が向上し、電解
を容易にする効果も期待できる。因みに、原料水中に塩
化ナトリウムや塩化カリウムの如きアルカリ金属中性塩
を添加しておくと、ナトリウムイオン(Na+ )やカリ
ウムイオン(K+ )は、電解作用により前述の通り陰極
に濃縮されて陰極水をアリカリ水となす作用をなすが、
他方の塩素イオン(Cl- )は、陽極側に濃縮されて塩
酸水を形成し、陽極水(オゾン水)を酸性化する事にな
る。この意味で、前記酸の添加に代えてアルカリ金属中
性塩を添加する事により、陽極側に弱酸性のオゾン水を
形成する事も可能であるが、前記アルカリ水の撒布によ
る培地への塩の蓄積を考慮すると、前述した酸の添加の
方が好ましい。The pH of the ozone water can be adjusted to be slightly acidic by making it possible to add the trace amount of acid to the vicinity of either the anode side raw material water inlet 26 or the ozone water outlet 28. In particular, if it is added in the anode-side raw water inlet 26, the electric conductivity of the raw water is improved, and an effect of facilitating electrolysis can be expected. By the way, if an alkali metal neutral salt such as sodium chloride or potassium chloride is added to the raw water, sodium ions (Na + ) and potassium ions (K + ) are concentrated on the cathode by the electrolytic action as described above. It has the function of making the cathode water and the alkaline water,
The other chlorine ion (Cl − ) is concentrated on the anode side to form a hydrochloric acid solution, thereby acidifying the anode water (ozone water). In this sense, it is possible to form a weakly acidic ozone water on the anode side by adding an alkali metal neutral salt instead of the addition of the acid. In view of the accumulation of acid, the addition of the acid described above is more preferable.
【0018】同様に、水の電解によって生成した水素イ
オン(H+ )は、陰極電極23側の電極面に集まって水
素ガスとなって水中から放出され、水素を含む陰極水と
して陰極水排出口29から前記陰極側排水管6を経て前
記陰極水撒布配管6aに送給される。Similarly, hydrogen ions (H.sup. + ) Generated by the electrolysis of water are collected on the electrode surface on the side of the cathode electrode 23, are released as hydrogen gas from the water, and are discharged as cathode water containing hydrogen as a cathode water outlet. From 29, the water is supplied to the cathode water spray pipe 6a through the cathode drain pipe 6.
【0019】因みに、前記電解式オゾン水製造装置1に
供給する原料水を軟水化処理するに当り、軟水化装置1
1としては、ナトリウムに代表されるアルカリ金属を用
いたアルカリ金属型イオン交換樹脂を用いる方式と、水
素型イオン交換樹脂を用いる方式とがあり、前者の場合
には、原水中のカルシウムやマグネシウムをアルカリ金
属に置換するものであるので、陰極面には水中に微量に
含まれているナトリウムイオン(Na+ )やカルシウム
イオン(Ca++)等のアルカリ金属イオンやアルカリ土
類金属イオンも集まって濃縮され、陰極側の水をアルカ
リ水となし、前述の水素ガスと共に陰極水排出口29か
らアルカリ水水を排出する事になる。述の配管12を経
てアルカリ水タンク3に送給される事になる。この様
に、陰極側には、水素ガスと共に水中に微量に含まれて
いるアルカリ金属イオンやアルカリ土類金属イオン(主
としてNa+ )も濃縮される結果、陰極側の水はpH9
〜11或いはそれ以上のアルカリ水が生成される事が確
認されている。一方、後者の場合には、原水中のカルシ
ウムやマグネシウムを水素に置換するので、アルカリ水
は生成されず、略中性の陰極水が排出される事になる。
尚、これらイオン交換樹脂の再生処理に当り、前者の場
合はナトリウムイオンを生成する食塩水で再生される
が、後者の場合には、水素イオンを生成する希塩酸や希
硫酸等を使用するため、これらの酸の保存や酸性排水処
理の問題が生じるので、ナトリウム型(アルカリ金属
型)イオン交換樹脂を用いるのが好ましい方式である。
以下は、係るアルカリ金属型イオン交換樹脂による軟水
化装置を用いて陰極側にアルカリ水を生成する場合の例
について説明する。Incidentally, when the raw water supplied to the electrolytic ozone water producing apparatus 1 is subjected to water softening treatment, the water softening apparatus 1
As 1, there are a method using an alkali metal type ion exchange resin using an alkali metal represented by sodium and a method using a hydrogen type ion exchange resin. In the former case, calcium and magnesium in raw water are removed. Alkali metal ions and alkaline earth metal ions such as sodium ions (Na + ) and calcium ions (Ca ++ ) contained in trace amounts in the water collect on the cathode surface because they are replaced with alkali metals. After being concentrated, the water on the cathode side is converted to alkaline water, and the alkaline water is discharged from the cathode water outlet 29 together with the hydrogen gas. The water is supplied to the alkaline water tank 3 via the pipe 12 described above. Thus, on the cathode side, the alkali metal ions and alkaline earth metal ions (mainly Na + ) contained in the water in trace amounts are also concentrated together with the hydrogen gas.
It has been confirmed that ~ 11 or more alkaline water is generated. On the other hand, in the latter case, calcium and magnesium in the raw water are replaced with hydrogen, so that no alkaline water is generated and almost neutral cathode water is discharged.
In the regeneration treatment of these ion exchange resins, the former is regenerated with a saline solution that generates sodium ions.In the latter case, dilute hydrochloric acid or dilute sulfuric acid that generates hydrogen ions is used. The use of a sodium-type (alkali metal-type) ion-exchange resin is a preferable method because problems such as preservation of these acids and treatment of acidic wastewater occur.
Hereinafter, an example in which alkaline water is generated on the cathode side using the water softening device using such an alkali metal ion exchange resin will be described.
【0020】尚、アルカリ金属型イオン交換樹脂を用い
る場合の陰極水のpH値は、両極側に供給する水の量の
比によって異なり、陰極側に供給する水の量を陽極側に
供給する水の量よりも少なくすれば、pH値は相対的に
高くなり、逆に多くすればpH値は低くする事が可能で
ある。The pH value of the cathode water when the alkali metal ion exchange resin is used varies depending on the ratio of the amount of water supplied to the two electrodes, and the amount of water supplied to the cathode is changed to the amount of water supplied to the anode. If the amount is smaller than the above, the pH value becomes relatively high, and if it is larger, the pH value can be lowered.
【0021】次に、図1において、上述した電解式オゾ
ン水製造装置1によって陽極側に生成したオゾン水はバ
ルブV2を経てオゾン水撒布配管5aに送給される。該
配管5aのバルブV4〜バルブV6から先の部分には、
植物を育成している複数のハウス4a〜4c内の上部に
配置され且つ多数の撒布ノズル7が設けられている。一
方、陰極水(アルカリ水)は、バルブV3を経て陰極水
撒布配管(以下『アルカリ水撒布配管』と記載する場合
がある)6aに送給される。該配管6aのバルブV7〜
バルブV9から先の部分は、前記複数のハウス4a〜4
c内の下部に配置され且つ多数の撒布ノズル8が設けら
れている。Next, in FIG. 1, the ozone water generated on the anode side by the above-mentioned electrolytic ozone water producing apparatus 1 is supplied to the ozone water spray pipe 5a via the valve V2. In a portion of the pipe 5a beyond the valves V4 to V6,
A large number of spray nozzles 7 are provided at the upper part of the plurality of houses 4a to 4c for growing plants. On the other hand, the cathode water (alkaline water) is supplied to a cathode water spray pipe (hereinafter sometimes referred to as “alkali water spray pipe”) 6a via a valve V3. Valves V7- of the pipe 6a
The portion beyond the valve V9 is connected to the plurality of houses 4a-4.
A large number of dispersing nozzles 8 are provided at a lower portion in the area c.
【0022】図2は、そのハウス内の配管と育成植物の
関係を示した概念図であって、ハウス内には所定間隔で
育成植物Pが植成されており、その上部には前記オゾン
水撒布配管5aが配置され、その下部には前記アルカリ
水撒布配管6aが設置されている。前記オゾン水撒布配
管5aには、前記育成植物Pの植成間隔と略同間隔でオ
ゾン水撒布ノズル7が配置され、オゾン水を育成植物P
の上部から該植物Pの地上部分に均一に撒布する様にな
っている。これにより、撒布されたオゾン水は育成植物
Pの茎葉に付着して、該茎葉に付着している病原菌を殺
菌する。同時に該オゾン水から気化したガスオゾンも、
育成植物Pの周りにオゾンガス含有空気層を短時間なが
ら形成し、オゾンガスによる殺菌と同様に、育成植物P
に付着している或いはその近傍に浮遊している病原菌の
殺菌に寄与する事になる。FIG. 2 is a conceptual diagram showing the relationship between the piping in the house and the growing plants. Growing plants P are planted at predetermined intervals in the house, and the ozone water A spray pipe 5a is arranged, and the alkaline water spray pipe 6a is installed below the spray pipe 5a. An ozone water spray nozzle 7 is disposed in the ozone water spray pipe 5a at substantially the same interval as the planting interval of the growing plant P, and the ozone water is sprayed from the growing plant P.
Of the plant P from the upper part of the plant P. Thereby, the sprayed ozone water adheres to the foliage of the growing plant P, and sterilizes the pathogenic bacteria adhering to the foliage. At the same time, gas ozone vaporized from the ozone water,
An ozone gas-containing air layer is formed around the growing plant P for a short time, and the sterilizing plant P
This contributes to the sterilization of pathogenic bacteria adhering to or floating near.
【0023】尚、本発明で使用するオゾン水は、オゾン
濃度が30ppm以下であり、従来のガス溶解方式で製
造されたオゾン水に比して比較的高濃度のオゾン水であ
るので、オゾン水濃度の自然減衰によりオゾン水が失効
するまでの時間が比較的長くなると共に、そのpHも弱
酸性の領域となしているので、長時間に亘ってオゾン水
濃度が維持される事になる。The ozone water used in the present invention has an ozone concentration of 30 ppm or less and is relatively high in concentration as compared with ozone water produced by a conventional gas dissolving method. Due to the natural decay of the concentration, the time until the ozone water expires is relatively long, and the pH is in a weakly acidic region, so that the ozone water concentration is maintained for a long time.
【0024】この点について説明すると、図4は、オゾ
ン水のpHとオゾン水中のオゾン濃度の経時変化を示し
たグラフであり、同図から明らかな通り、アルカリ領域
では急速にオゾン濃度が低下する事が分かる。即ち、中
性領域及び酸性領域では、オゾン濃度の急激な低下を防
止し得る事が理解される。本発明は、係る知見に基づい
てオゾン水のpHを、最もオゾン濃度の減衰の小さな弱
酸性となしている。好ましいpHとしてはpH3以上,
7未満であり、アルカリ領域では、上述の通りオゾン水
の分解が促進されるので、オゾン水撒布までの移送中に
オゾンが分解して失効し、オゾン水の撒布には適さない
からである。又、pHを3以上としたのは、酸性度が高
いオゾン水を長期間に亘って撒布し続けると、育成植物
に悪影響がでる事は酸性雨の問題と同様である。従っ
て、pHは3以上、好ましくは5以上の弱酸性に調整す
るのがよい。FIG. 4 is a graph showing the change over time in the pH of the ozone water and the ozone concentration in the ozone water. As is clear from FIG. 4, the ozone concentration rapidly decreases in the alkaline region. I understand that. That is, it is understood that a sharp decrease in the ozone concentration can be prevented in the neutral region and the acidic region. According to the present invention, the pH of the ozone water is set to be weakly acidic with the smallest attenuation of the ozone concentration based on such knowledge. The preferred pH is pH 3 or higher,
Since it is less than 7 and the decomposition of ozone water is promoted in the alkaline region as described above, ozone is decomposed and invalidated during transfer up to the spraying of ozone water, and is not suitable for spraying ozone water. The reason why the pH is set to 3 or more is that, as long as ozone water having a high acidity is continuously sprayed over a long period of time, the growing plants are adversely affected as in the case of acid rain. Therefore, the pH is preferably adjusted to a weak acidity of 3 or more, preferably 5 or more.
【0025】因みに、上述の説明では、電解式オゾン水
製造装置1で生成したオゾン水を、直接オゾン水撒布配
管5aに供給して撒布する様にしているが、図1に示し
ている様に、該オゾン水製造装置1で生成したオゾン水
は、バルブV10を経て一旦オゾン水タンク2に貯蔵し
た後にバルブV11及びポンプP1を経て前記オゾン水
撒布配管5aに供給する様になす事も可能である。この
場合には、オゾン水タンク2内におけるオゾン水貯蔵期
間中に、オゾンが分解してオゾン濃度が低下するのは極
力避けなければならない。そこで、本発明では、オゾン
水タンク2は密閉構造のタンクとしている。この点を図
5により説明する。図5は、弱酸性領域でのオゾン水中
のオゾン濃度の経時変化を示したグラフであって、オゾ
ン水中に酢酸を添加してpH4の弱酸性に調整したもの
で、(a)はこのオゾン水をステンレス容器に充填率1
00%で充填した場合のオゾン濃度の変化を示し、
(b)は上部を開放した三つ口フラスコの底部にオゾン
水を注入して放置した場合(フラスコの開口部には栓を
せずに開放)のオゾン濃度の変化を示し、(c)は前記
(b)と同様の三つ口フラスコの底部にオゾン水を注入
し、中央の開口には栓をして両側の開口の一方から空気
を流入させ他方の開口から流出する様にした場合のオゾ
ン濃度の変化を変化を示している。同図から明らかな様
に、密閉系(a)では30分経過後も約4.9mol/
l(減少率約4%)であるのに対し、単なる開放系
(b)では約2.2mol/l(減少率約60%),気
体流通系(c)では約0.4mol/l(減少率約90
%)となっている。この事から、オゾン水を弱酸性領域
で密閉系に保持しておけば、オゾンの自然分解や自然放
散等による自然減衰速度を大幅に低減させる事が可能で
ある事が理解されよう。従って、オゾン水を貯蔵して移
送する場合には、貯蔵タンクは密閉タンクとなすのが好
ましいといえる。Incidentally, in the above description, the ozone water generated by the electrolytic ozone water producing apparatus 1 is supplied directly to the ozone water distributing pipe 5a to be sprinkled. However, as shown in FIG. The ozone water generated by the ozone water producing apparatus 1 can be stored in the ozone water tank 2 via a valve V10 and then supplied to the ozone water spray pipe 5a via a valve V11 and a pump P1. . In this case, during the ozone water storage period in the ozone water tank 2, the degradation of ozone and the decrease in ozone concentration must be avoided as much as possible. Therefore, in the present invention, the ozone water tank 2 is a tank having a closed structure. This will be described with reference to FIG. FIG. 5 is a graph showing the change over time of the ozone concentration in the ozone water in the weakly acidic region, in which acetic acid was added to the ozone water to adjust the pH to a weakly acidic one, and (a) shows the ozone water. Filling rate in stainless steel container
Shows the change in ozone concentration when filled at 00%,
(B) shows the change in ozone concentration when ozone water was injected into the bottom of a three-necked flask with an open top and left standing (opened without opening the opening of the flask), and (c) shows the change in ozone concentration. In the case where ozone water is injected into the bottom of the same three-necked flask as in (b) above, and the center opening is plugged so that air flows in from one of the openings on both sides and flows out from the other opening. The change in ozone concentration is shown as a change. As is clear from the figure, in the closed system (a), about 4.9 mol /
1 (decrease rate of about 4%), whereas in the simple open system (b) it is about 2.2 mol / l (decrease rate about 60%), and in the gas flow system (c) it is about 0.4 mol / l (decrease rate). About 90
%). From this, it can be understood that if ozone water is kept in a closed system in a weakly acidic region, the natural decay rate due to the natural decomposition and natural emission of ozone can be greatly reduced. Therefore, when storing and transferring ozone water, it can be said that the storage tank is preferably a closed tank.
【0026】尚、実際のタンクでは、オゾン水充填率が
100%の状態は稀であり、空気のベント管が配置され
て蓋がなされているのが一般的なタンク構造であるが、
タンク内の気液は、次第にオゾンの平衡状態に近付いて
くるので、オゾン水製造装置からオゾン水が該タンク内
に供給されつつ該タンクからオゾン水を排出する様な場
合には、前記タンク内のオゾン水濃度は、上記(a)と
(b)との中間的な挙動を示す事になる。従って本発明
では蓋をした状態のタンクを含めて「密閉系」として記
載する。又、好ましいものとしては、オゾン水タンクに
オゾン水を加圧下で供給し、該オゾン水を加圧下で保持
できるものがある。この場合には、密閉系に加えて加圧
系であるので、オゾン水濃度の低下を長時間に亘って防
止可能となり、オゾン水を撒布地に輸送するには最適の
ものである。In an actual tank, the state where the ozone water filling rate is 100% is rare, and it is a general tank structure that an air vent pipe is disposed and a lid is formed.
The gas-liquid in the tank gradually approaches the equilibrium state of ozone. Therefore, when the ozone water is discharged from the tank while the ozone water is supplied from the ozone water producing apparatus into the tank, the inside of the tank is The ozone water concentration indicates an intermediate behavior between the above (a) and (b). Therefore, in the present invention, the term “closed system” including the tank with a lid is described. Further, as a preferable example, there is a type in which ozone water is supplied to an ozone water tank under pressure and the ozone water can be held under pressure. In this case, since the system is a pressurized system in addition to the closed system, a decrease in ozone water concentration can be prevented over a long period of time, which is optimal for transporting ozone water to a spraying site.
【0027】以上の通り、比較的高濃度で弱酸性に調整
されたオゾン水を、前記育成植物Pの地上部に撒布する
と、該育成植物Pに撒布された時のオゾン水濃度も相当
高い値に維持されており、従って、オゾンによる殺菌効
果を高く且つ長時間維持する事が可能となっている。
又、オゾン水が生成されてから撒布される迄の許容時間
も前述の通り長く取れるので、オゾン水製造装置1の設
置場所と撒布場所4とが離れていても、オゾン水の移送
過程におけるオゾン濃度の減衰も最小限に止める事も可
能となっている。尚、前記オゾン水濃度は、オゾン水製
造装置と撒布場所との関係で考慮されるべきであり、オ
ゾン水製造装置から直接撒布される場合には、オゾン水
濃度が2〜10ppm程度でもよいが、図1の如くオゾ
ン水製造装置と撒布場所とが離れている場合には、その
移送時間に応じて高い濃度のオゾン水を用いるべきであ
り、通常は5〜30ppm程度の範囲で選定されるのが
好ましい。尚、オゾン水濃度が高過ぎると、育成植物の
茎葉表面或いはその近傍で気化したオゾンガスが、葉の
気孔を通して葉肉の内部に侵入し、葉の組織を破壊する
可能性が高くなるので、30ppm以下となす必要があ
り、好ましくは20ppm以下がよい。尚、植物に対す
る限界オゾン水濃度は、植物の種類や成育段階によって
も異なり、又、最適オゾン水濃度も、前述の植物の種類
や成育段階と共に対象とする病害の種類によっても異な
るので、実験等により適宜選定すべきものである事はい
うまでもない。As described above, when the relatively high concentration of ozone water adjusted to be weakly acidic is sprayed on the aerial part of the cultivated plant P, the ozone water concentration when scattered on the cultivated plant P is considerably high. Therefore, it is possible to maintain a high sterilizing effect of ozone for a long time.
In addition, since the allowable time from the generation of the ozone water to the spraying can be made long as described above, even if the installation place of the ozone water production apparatus 1 and the spraying place 4 are far from each other, the ozone in the transfer process of the ozone water is not required. It is also possible to minimize the concentration decay. In addition, the ozone water concentration should be considered in relation to the ozone water production device and the spraying place. When the ozone water concentration is directly sprayed from the ozone water production device, the ozone water concentration may be about 2 to 10 ppm. As shown in FIG. 1, when the ozone water producing apparatus and the spraying place are separated from each other, ozone water having a high concentration should be used according to the transfer time, and is usually selected in a range of about 5 to 30 ppm. Is preferred. If the ozone water concentration is too high, the possibility that ozone gas vaporized on or near the foliage surface of the cultivated plant penetrates into the mesophyll through the stomata of the leaves and destroys the leaf tissue becomes high, so that 30 ppm or less. And preferably 20 ppm or less. The limit ozone water concentration for plants differs depending on the type and growth stage of the plant, and the optimum ozone water concentration also differs depending on the type of disease to be treated as well as the type of plant and the growth stage described above. Needless to say, it should be selected as appropriate.
【0028】次に、前記アルカリ水撒布配管6には、ア
ルカリ水撒布ノズル8が、1つの育成植物Pの両側に位
置する様に夫々配置されており、前記育成植物Pの根元
部或いはその近傍にアルカリ水が撒布される様になって
いる。これには幾つかの理由があり、第一には、前記オ
ゾン水撒布ノズル7から撒布されたオゾン水が弱酸性で
あるので、該弱酸性水が育成植物Pを伝わって土壌Gに
侵入するのは避けられない。そこで、土壌Gが酸性化す
るのを該アルカリ水で中和する目的を有するものであ
る。次に、第二には、比較的高濃度のオゾン水が、育成
植物を伝わって或いは直接土壌に撒布されるのは避けら
れないが、このオゾン水により土壌表面近傍の各種有効
微生物をも殺菌してしまう可能性がある。そこで、アル
カリ水を地表面に撒布してオゾン水と接触させる事によ
って、前述の通りオゾンの分解を促進させてオゾン水の
殺菌機能を速やかに失効させる目的を有するものであ
る。Next, in the alkaline water spray pipe 6, alkaline water spray nozzles 8 are respectively disposed so as to be located on both sides of one growing plant P, and a root portion of the growing plant P or in the vicinity thereof. Is sprayed with alkaline water. There are several reasons for this. Firstly, since the ozone water sprayed from the ozone water spray nozzle 7 is weakly acidic, the weakly acidic water travels through the growing plant P and enters the soil G. It is inevitable. Therefore, the purpose of the present invention is to neutralize acidification of the soil G with the alkaline water. Second, it is inevitable that a relatively high concentration of ozone water is transmitted through the growing plant or directly spread on the soil, but this ozone water also kills various effective microorganisms near the soil surface. Could be done. Thus, by spraying alkaline water on the ground surface and bringing it into contact with ozone water, as described above, it has the purpose of promoting the decomposition of ozone and quickly invalidating the sterilizing function of ozone water.
【0029】以上は、ハウス内の育成植物にオゾン水を
撒布する例であるが、果樹園等の屋外の山野において育
成している植物に対しては、その撒布場所までオゾン水
を搬送するか、現地にてオゾン水を製造するかのいずれ
かの方式となる。係る果樹園等には、収穫時の果実の搬
送や各種農薬及び肥料の搬入のために、少なくとも小型
トラックが進入可能な程度の道路が設けられている。そ
こで、図6に示した様に、小型トラック40の荷台に、
原料水タンク42と該原料水の軟水化装置11と電解式
オゾン水製造装置1と該電解式オゾン水製造装置に必要
な電力を発生する発電装置41とを搭載して移動式オゾ
ン水撒布装置となしている。この装置において、前記原
料水タンク42に水道水等の適宜の原料水を適量注水し
て果樹園等のオゾン水撒布を行う現場に車両40に搭載
して搬入する。現地では、ガソリン,灯油或いは太陽電
池等で小型の発電装置41を作動させて電解式オゾン水
製造装置1を稼働させ、前記原料水タンク42内の原料
水を軟水化装置11を経て該電解式オゾン水製造装置1
に供給して水の電解を行い、前述した様に、陽極側にオ
ゾン水が、陰極側にアルカリ水が生成する。前記電解式
オゾン水製造装置1にはオゾン水排出ノズル1aとアル
カリ水排出ノズル1bとが配置されており、夫々に、先
端に撒布ノズルを有する配管を接続し、オゾン水は前述
の要領で樹木の地上部に、アルカリ水は該樹木の根元部
或いはその近傍に夫々撒布する。The above is an example in which ozone water is sprayed on growing plants in a house. For plants growing in an outdoor mountain field such as an orchard, whether or not ozone water is to be transported to the spraying place is determined. , Or ozone water is produced locally. In the orchard or the like, a road is provided at least to the extent that a small truck can enter in order to transport fruits at the time of harvesting and to carry in various pesticides and fertilizers. Therefore, as shown in FIG.
A mobile ozone water spraying apparatus equipped with a raw water tank 42, a water softening device 11 for the raw water, an electrolytic ozone water producing device 1, and a power generating device 41 for generating electric power required for the electrolytic ozone water producing device. And that. In this apparatus, a suitable amount of raw water such as tap water is injected into the raw water tank 42 in an appropriate amount, and the vehicle is mounted on a vehicle 40 and carried into a site where ozone water is sprayed such as an orchard. In the field, a small power generator 41 is operated by gasoline, kerosene, a solar cell or the like to operate the electrolytic ozone water producing apparatus 1, and the raw water in the raw water tank 42 is passed through the water softening apparatus 11 to the electrolytic water. Ozone water production equipment 1
And ozone water is generated on the anode side and alkaline water is generated on the cathode side, as described above. The electrolytic ozone water producing apparatus 1 is provided with an ozone water discharge nozzle 1a and an alkaline water discharge nozzle 1b, each of which is connected to a pipe having a spray nozzle at a tip thereof, and the ozone water is supplied to a tree as described above. Alkaline water is sprayed on or above the root of the tree.
【0030】係る移動式オゾン水撒布装置を所定の場所
まで搬送し、その場で撒布作業を行う場合には、前記オ
ゾン水排出ノズル1a及びアルカリ水排出ノズル1bの
夫々に、先端に撒布ノズルを備えたビニールホース等の
可撓性ホースを接続し、1人がオゾン水の撒布を、他の
1人はアルカリ水の撒布を行う。尚、1人で撒布作業を
行う場合には、オゾン水撒布中は、前記アルカリ水は地
表に垂れ流しする事も可能であるが、アルカリ水はオゾ
ン水と異なり、分解する事はないので、適宜の空タンク
を用意しておき、オゾン水散布中は、該タンクにアルカ
リ水を溜めておき、オゾン水散布終了後にアルカリ水の
散布を行う様になす事も可能である。一方、前記オゾン
水排出ノズル1a及びアルカリ水排出ノズル1bの夫々
に、先端に撒布ノズルを備えた固定式の配管を設け、車
両を移動させつつオゾン水やアルカリ水の撒布を行う事
も可能である。特に、この方式は、街路樹に対するオゾ
ン水やアルカリ水の撒布には最適である。When the mobile ozone water spraying device is transported to a predetermined place and the spraying operation is performed on the spot, a spraying nozzle is provided at the tip of each of the ozone water discharge nozzle 1a and the alkaline water discharge nozzle 1b. A flexible hose such as a vinyl hose provided is connected, and one person sprays ozone water and the other person sprays alkaline water. In the case where the spraying operation is performed by one person, during the spraying of the ozone water, the alkaline water may be allowed to run down to the surface of the ground. However, unlike the ozone water, the alkaline water does not decompose. It is also possible to prepare an empty tank and store the alkaline water in the tank during the spraying of the ozone water, and to spray the alkaline water after the spraying of the ozone water is completed. On the other hand, each of the ozone water discharge nozzle 1a and the alkaline water discharge nozzle 1b may be provided with a fixed pipe having a spray nozzle at the tip, and spray ozone water or alkaline water while moving the vehicle. is there. In particular, this method is most suitable for spraying ozone water or alkaline water on street trees.
【0031】尚、上記において、原料水タンク42に、
予め軟水化処理した軟水を充填する方式も可能であり、
この場合には、前記軟水化装置11は車両40に搭載不
要となる事は言うまでもない。In the above description, the raw water tank 42
It is also possible to fill with soft water that has been softened in advance,
In this case, it goes without saying that the water softening device 11 does not need to be mounted on the vehicle 40.
【0032】次に、本発明の実施例について説明する。
以下の実施例では、オゾン水撒布による植物の病害防除
効果を確認するため、キュウリ葉に図3に示した電解式
オゾン水製造装置で製造されたオゾン水を撒布して「キ
ュウリうどんこ病(以下、単に『うどんこ病』と記載す
る」の防除効果を調査すると共に、該オゾン水撒布によ
る「光合成抑制」の有無についても調査するためオゾン
水撒布の前後のキュウリ葉の純光合成速度を測定した。Next, an embodiment of the present invention will be described.
In the following examples, in order to confirm the disease control effect of plants by spraying ozone water, cucumber leaves were sprayed with ozone water produced by the electrolytic ozone water producing apparatus shown in FIG. In the following, the control effect of "merely described as powdery mildew" was investigated, and the net photosynthetic rate of cucumber leaves before and after the ozone water spraying was measured to investigate the presence or absence of "photosynthesis suppression" by the ozone water spray. did.
【0033】[0033]
【実施例】供試植物として、キュウリ株(品種:シャー
プ7)を用い、キュウリ株の栽培は、東京大学農学部内
の屋上ガラス温室で行った。培地には樹皮加工植物栽培
支持材を用い、灌水を兼ねた養液には大塚ハウスB処方
1単位養液の供給を、1株当り0.2l、1日1回行っ
た。尚、このキュウリ株の葉にうどんこ病原菌を塗布し
てうどんこ病の発病を促進した。供試植物と栽培条件の
詳細は、表1の通りである。EXAMPLE A cucumber strain (variety: Sharp 7) was used as a test plant, and the cucumber strain was cultivated in a rooftop glass greenhouse in the Faculty of Agriculture, the University of Tokyo. A bark-processed plant cultivation support material was used as a medium, and Otsuka House B prescription 1 unit nutrient solution was supplied at a rate of 0.2 L per share once a day as a nutrient solution also serving as irrigation. The pathogen of powdery mildew was applied to the leaves of this cucumber strain to promote the onset of powdery mildew. Table 1 shows details of test plants and cultivation conditions.
【0034】[0034]
【表1】 [Table 1]
【0035】前記試験区には、試験水の撒布を行わなか
った「Cont区」と、蒸留水を撒布した「DW区」と
オゾン濃度2ppmのオゾン水を撒布した「O3-2区」
とオゾン濃度4ppmのオゾン水を撒布した「O3-4
区」の計4試験区とした。撒布した試験水(蒸留水及び
オゾン水)の詳細は、表2の通りである。尚、使用した
オゾン水製造装置は、神鋼プラント建設(株)製の高濃
度オゾン水製造装置(Do−03型)を用いた。In the test section, a “Cont section” where test water was not sprayed, a “DW section” where distilled water was sprayed, and an “O 3 -2 section” where ozone water having an ozone concentration of 2 ppm was sprayed.
O 3 -4 sprayed with ozone water with an ozone concentration of 4 ppm
Ward ”for a total of 4 test plots. Details of the test water (distilled water and ozone water) sprayed are as shown in Table 2. The ozone water producing apparatus used was a high concentration ozone water producing apparatus (Do-03 type) manufactured by Shinko Plant Construction Co., Ltd.
【0036】[0036]
【表2】 [Table 2]
【0037】オゾン水の撒布は、肩掛式噴霧器(NH9
D,(株)丸山製作所製)を用いて、1鉢当り0.15
lを週に2回行った。撒布に当り、培地にオゾン水が触
れない様に培地表面を透明プラスチックフィルムで被覆
した。うどんこ病発病度(以下単に「発病度」と記載す
る)は、展開葉の全てについて目視により、表3に示し
た5段階評価法に基づいて評価した値から、次式(1)
を用いて算定した。The spraying of the ozone water is performed using a shoulder-type sprayer (NH9).
D, manufactured by Maruyama Manufacturing Co., Ltd.)
1 twice a week. At the time of spraying, the surface of the medium was covered with a transparent plastic film so that ozone water did not touch the medium. The degree of powdery mildew (hereinafter simply referred to as “degree of disease”) is calculated from the value of all developed leaves visually evaluated based on the five-step evaluation method shown in Table 3 and the following equation (1).
It was calculated using.
【0038】[0038]
【数1】 (Equation 1)
【0039】[0039]
【表3】 [Table 3]
【0040】一方、純光合成速度は、携帯用光合成蒸散
測定装置(LI−6400,米国LI−COR社製)を
用いて、異なる光強度(PPFD300及び500μm
ol・m-2・s-1)下で測定した。On the other hand, the net photosynthetic rate was measured at different light intensities (PPFD 300 and 500 μm) using a portable photosynthesis and evaporation measurement device (LI-6400, manufactured by LI-COR, USA).
ol · m -2 · s -1 ).
【0041】上記試験による病害防除結果を示した図7
から明らかな様に、オゾン水を撒布していない「Con
t区」及び「DW区」の発病度は、試験開始後徐々に増
加しているのに対し、オゾン水を撒布した「O3-2区」
及び「O3-4区」の発病度は略一定で推移している。試
験最終日における「O3-2区」及び「O3-4区」の発病
度は、「Cont区」及び「DW区」の発病度よりも夫
々1%レベルで有意に小であった。尚、「O3-2区」と
「O3-4区」の発病度には有意差は認められなかった
が、オゾン水の撒布により、発病度を低下させ得る大き
な防除効果が期待出来る事が分かった。FIG. 7 showing the results of disease control by the above test.
As is evident from the figure, "Con
The disease rates of the “t section” and “DW section” gradually increased after the start of the test, while the “O 3 -2 section” to which ozone water was sprayed was used.
And the incidence of disease in the “O 3 -4 ward” has remained almost constant. On the last day of the test, the disease rates of the “O 3 -2 section” and “O 3 -4 section” were significantly smaller at the 1% level than those of the “Cont section” and “DW section”, respectively. There was no significant difference in the disease incidence between the “O 3 -2 section” and the “O 3 -4 section”. However, by spraying ozone water, a large control effect that can lower the disease degree can be expected. I understood.
【0042】次に、オゾン水撒布による純光合成抑制に
ついては、上記試験結果を図8及び図9に示した様に、
前記光強度(PPFD300及び500μmol・m-2
・s -1)下にはオゾン水撒布の前後に大きな差は認めら
れず、又、僅かに認められる差も「Cont区」及び
「DW区」のそれと同程度であり、オゾン水撒布による
光合成の抑制は認められなかった。Next, to suppress pure photosynthesis by spraying ozone water.
As shown in FIG. 8 and FIG.
The light intensity (PPFD 300 and 500 μmol · m-2
・ S -1) Below, a large difference was observed before and after ozone water spraying.
And the slight difference was observed in the “Cont section” and
It is almost the same as that of "DW ward", and is sprayed with ozone water.
No inhibition of photosynthesis was observed.
【0043】又、この試験の結果、弱酸性のオゾン水を
撒布しても、電解強酸性陽極水の撒布によりしばしば発
生が認められる葉焼け様の生理障害(葉の黄化・褐変)
は認められなかった。In addition, as a result of this test, even when slightly acidic ozone water is sprayed, leaf scald-like physiological disorders (yellowing / browning of leaves) often observed due to spraying of strongly acidic electrolytic anolyte water.
Was not found.
【0044】以上の試験結果から、オゾン水の撒布はう
どんこ病の防除に有効であり、且つキュウリ葉に対して
も光合成抑制や生理障害発生等の負の影響を及ぼさない
事が明らかになった。この事実から、オゾン水は植物の
他の病害防除にも有効な事が容易に推察される。又、オ
ゾン水濃度も2〜4ppmで相当の効果があったが、更
に高濃度の10ppm程度のものを使用すれば、更に顕
著な効果が現れるものと考えられる。From the above test results, it was clarified that the spraying of ozone water was effective for controlling powdery mildew and had no negative effect on cucumber leaves, such as suppression of photosynthesis and occurrence of physiological disorders. Was. From this fact, it is easily presumed that ozone water is also effective in controlling other diseases of plants. Although the ozone water concentration was considerably high at 2 to 4 ppm, it is considered that a more remarkable effect appears when a higher concentration of about 10 ppm is used.
【0045】本発明は以上の通り、比較的高濃度のオゾ
ン水を弱酸性に調整して育成植物の地上部に撒布する事
により植物の病害防除を行うものであって、上記した説
明例に限定されるものではなく、種々の応用例や変形例
が存在する事は言うまでもない。例えば、図2の例で
は、オゾン水撒布配管5aに所定間隔で撒布ノズル7を
配置しているが、育成植物Pの種類が変わった場合に
は、そのノズル間隔を育成植物Pの間隔に応じて調整可
能な構造となすのが一般的である。この場合には、撒布
配管5aを伸縮自在となすか或いは該撒布配管をビニー
ルホース等の可撓性を有する材料で形成し、その弛み度
合いを適宜調整する事により、該ノズル間隔を調整可能
となす事も可能である。更に、前記撒布ノズル7を1つ
のみとなし、これを育成植物の上部で移動式にして順次
移動させつつオゾン水撒布を行う様になす事も可能であ
る。As described above, the present invention is intended to control a plant disease by adjusting a relatively high concentration of ozone water to be weakly acidic and spraying it on the aerial part of a growing plant. It is needless to say that the present invention is not limited thereto, and that there are various applications and modifications. For example, in the example of FIG. 2, the spray nozzles 7 are arranged at predetermined intervals in the ozone water spray pipe 5a, but when the type of the growing plant P changes, the nozzle interval is changed according to the interval of the growing plant P. In general, the structure is adjustable. In this case, the nozzle interval can be adjusted by making the distributing pipe 5a expandable or contractible or by forming the distributing pipe from a flexible material such as a vinyl hose and appropriately adjusting the degree of slack. It is also possible to do. Furthermore, it is also possible to use only one spray nozzle 7 and to move the ozone water above the growing plant so as to sequentially spray the ozone water.
【0046】又、ハウス栽培の育成植物にオゾン水を撒
布する場合には、本発明で使用するオゾン水の濃度は比
較的高濃度であるから、作業員がハウス内に入って撒布
するのは好ましくない。従って、図1,2に示している
如く、オゾン水製造装置やオゾン水タンクをハウス外に
設置しておき、オゾン水撒布配管のみをハウス内に設置
して、作業員がハウス内に入らなくても全ての操作をハ
ウス外で行える様になすのが好ましい。In the case of spraying ozone water on growing plants grown in a house, the concentration of ozone water used in the present invention is relatively high. Not preferred. Therefore, as shown in FIGS. 1 and 2, the ozone water producing apparatus and the ozone water tank are installed outside the house, and only the ozone water spraying pipe is installed inside the house, so that the worker does not enter the house. However, it is preferable that all operations can be performed outside the house.
【0047】又、ミカン,ぶどう,梨,桃等の屋外栽培
の果樹園の場合でも、当該果樹園の近傍に車載式オゾン
水製造装置を搬入し、該装置から可撓性ホースで各樹木
の地上部に向けてオゾン水を撒布する様になす事は前述
の通りであるが、山間部の果樹園の場合には、灌水用の
配管が既に配置されている場合も多いので、この場合に
は、該配管を通してオゾン水を送水し、該配管の各所に
配置されている蛇口から、現在農薬撒布に使用されてい
る肩掛式の噴霧器にオゾン水を分取して各樹木に撒布す
る事も可能である。係る方式が可能となるのは、本発明
で使用するオゾン水が比較的高濃度である事とオゾンの
自然分解が抑制される様にpH調整を行っている事によ
る。In the case of orchards grown outdoors, such as oranges, grapes, pears, peaches, etc., an on-vehicle type ozone water producing apparatus is carried in the vicinity of the orchard, and each tree is fed from the apparatus with a flexible hose. As described above, ozone water is sprayed toward the above-ground part.In the case of orchards in mountainous areas, irrigation pipes are often already installed, so in this case, It is also possible to send ozone water through the pipe, and to collect ozone water from faucets located at various places in the pipe to a shoulder-type sprayer currently used for pesticide spraying and spray it on each tree. It is. Such a system becomes possible because the ozone water used in the present invention has a relatively high concentration and the pH is adjusted so that the natural decomposition of ozone is suppressed.
【0048】又、育成植物の群の内の発病が認められた
一部にのみオゾン水を撒布する場合には、前記肩掛式の
噴霧器にオゾン水を充填して現場に搬送したり、或い
は、タンクに充填して現場近傍に搬送し、その場で前記
噴霧器にオゾン水を分取して撒布する事も可能である。
この場合には、オゾン水の自然分解速度を抑制するため
に、酸性度を高めておき、現場で水を配合してpH調整
を行う様にする事も可能である。In the case where ozone water is sprayed only on a part of the group of growing plants where disease is observed, the shoulder-type sprayer is filled with ozone water and transported to the site, or It is also possible to fill the tank and transport it near the site, whereupon the ozone water is fractionated and sprayed on the sprayer.
In this case, in order to suppress the natural decomposition rate of the ozone water, the acidity may be increased, and the pH may be adjusted by adding water on site.
【0049】又、オゾン水のpH調整に当り、酸を添加
してpH調整を行う場合には、目的とする植物が成育途
上にあるときは、希塩酸や希硫酸等の安価な強酸の希釈
水溶液を用いて調整する事も可能であるが、収穫前に
は、係る硫酸や塩酸は好ましくないので、仮に人体に入
ったとしても影響のない酢酸やクエン酸やリンゴ酸等の
安全な弱酸でpH調整するのが好ましい。When adjusting the pH of ozone water by adding an acid, if the target plant is growing, an inexpensive diluted aqueous solution of a strong acid such as dilute hydrochloric acid or dilute sulfuric acid is used. It is possible to adjust the pH with a safe weak acid such as acetic acid, citric acid or malic acid, which is not affected even if it enters the human body. Adjustment is preferred.
【0050】[0050]
【発明の効果】以上説明した如く、本発明のオゾン水に
よる植物の病害防除方式によると、比較的高濃度のオゾ
ン水を用いるので、オゾンによる殺菌効果の保持時間を
長くする事ができるのみならず、オゾン水のpHもオゾ
ン水濃度の自然減衰を抑制できる弱酸性に調整している
ので、オゾンによる殺菌効果を、一層長時間に亘って保
持する事ができ、撒布後も確実に植物の病害防除効果が
維持される事になる。As described above, according to the method for controlling plant diseases using ozone water according to the present invention, since a relatively high concentration of ozone water is used, it is possible to prolong the holding time of the sterilization effect by ozone. In addition, the pH of the ozone water is adjusted to a weak acidity that can suppress the natural decay of the ozone water concentration, so that the sterilizing effect of ozone can be maintained for a longer time, and the plant can be reliably planted even after spraying. Disease control effect will be maintained.
【0051】又、オゾン水のpH調整により、オゾン水
濃度を有効な範囲に長時間保持できるので、オゾン水製
造場所から撒布場所が離れている様な場合でも、オゾン
水の輸送が可能となり、オゾン水撒布による病害防除の
対象も適宜拡大する事が可能となり、無農薬化,減農薬
化に大きく貢献する事が期待される。特に、オゾン水製
造装置から送給されるオゾン水をタンクに貯留する方式
を採用する場合には、該タンクを実質的に密閉構造とな
す事により、タンク内での貯留期間内におけるオゾン水
濃度の自然減衰を抑制できるので、上記pH調整との相
乗効果により、オゾン水の一層の長距離輸送も可能とな
り、オゾン水撒布対象の一層の拡大も可能となる。Further, since the ozone water concentration can be maintained in an effective range for a long time by adjusting the pH of the ozone water, even if the spraying place is far from the ozone water production place, the ozone water can be transported. The target of disease control by spraying ozone water can be expanded as appropriate, and it is expected to greatly contribute to eliminating pesticides and reducing pesticides. In particular, when adopting a method of storing ozone water sent from an ozone water production device in a tank, the tank is made substantially sealed so that the ozone water concentration during the storage period in the tank is reduced. Since the natural attenuation can be suppressed, the synergistic effect with the above-mentioned pH adjustment enables the ozone water to be transported over a longer distance, and the object to be sprayed with the ozone water can be further expanded.
【0052】又、オゾン水製造装置として水の電解によ
るオゾン水製造装置を用いる場合には、陽極側のオゾン
水と共に、陰極側にはアルカリ水が生成するので、この
アルカリ水を、従来の灌水に代えて植物の根元又はその
近傍に撒布する様になせば、前記地表面に落下した弱酸
性のオゾン水の中和作用と、該弱酸性のオゾン水のpH
を高めてオゾンの自然分解速度を速め、オゾン水による
地表近傍の有効微生物の殺菌という負の障害も防止でき
る効果がある。When an ozone water producing apparatus by electrolysis of water is used as the ozone water producing apparatus, alkaline water is generated on the cathode side together with the ozone water on the anode side. Instead of spraying on the root of the plant or in the vicinity thereof, the neutralizing action of the weakly acidic ozone water dropped on the ground surface and the pH of the weakly acidic ozone water
To increase the natural decomposition rate of ozone and prevent the negative obstacle of sterilizing effective microorganisms near the ground surface with ozone water.
【0053】更に、オゾン水製造装置を原料水タンク及
び発電装置と共に車両に搭載して移動式となせば、果樹
園等の広大な耕地内に育成されている植物に対しても、
順次車両を移動させつつ撒布する事も可能となり、オゾ
ン水による植物の病害防除システムの適用範囲を可及的
に拡大可能となる。Further, if the ozone water producing apparatus is mounted on a vehicle together with a raw water tank and a power generation apparatus to be mobile, even if the plant is grown in a vast arable land such as an orchard,
It is also possible to spread the vehicle while moving it sequentially, and it becomes possible to expand the application range of the plant disease control system using ozone water as much as possible.
【0054】特に、従来から環境面や健康面から何かと
問題視されている農薬の使用が不要となったり或いは少
なくとも減少させる事が可能となるので、人の健康のみ
ならず、昆虫その他の動植物に対する悪影響も軽減され
る等、本発明による社会,環境に及ぼす効果は大なるも
のが期待される。In particular, since the use of pesticides, which has been regarded as a problem in terms of the environment and health, can be eliminated or at least reduced, not only human health but also insects and other animals and plants can be reduced. The effect of the present invention on society and the environment is expected to be great, for example, adverse effects are reduced.
【図1】本発明に係る植物の病害防除方法を実施するた
めの植物の病害防除装置の一例を示すフロー図である。FIG. 1 is a flowchart showing an example of a plant disease control apparatus for carrying out a plant disease control method according to the present invention.
【図2】図1に示した植物栽培ハウス内における陽極水
(オゾン水)撒布配管及び陰極水(アルカリ水)撒布配
管の例を示す概念図である。FIG. 2 is a conceptual diagram showing an example of an anode water (ozone water) spray pipe and a cathode water (alkali water) spray pipe in the plant growing house shown in FIG.
【図3】本発明で使用する電解式オゾン水製造装置の要
部概略図である。FIG. 3 is a schematic view of a main part of an electrolytic ozone water producing apparatus used in the present invention.
【図4】各種pHにおけるオゾン水濃度の経時変化を示
すグラフである。FIG. 4 is a graph showing changes over time in ozone water concentration at various pHs.
【図5】密閉系と大気開放系と大気流通系におけるオゾ
ン水濃度の経時変化を示すグラフである。FIG. 5 is a graph showing changes over time in ozone water concentration in a closed system, an open air system, and an air circulation system.
【図6】本発明で使用する可搬式オゾン水撒布装置の一
例を示す概念図である。FIG. 6 is a conceptual diagram showing an example of a portable ozone water spraying apparatus used in the present invention.
【図7】本発明によるオゾン水撒布による病害防除効果
を示すグラフである。FIG. 7 is a graph showing a disease control effect by spraying ozone water according to the present invention.
【図8】オゾン水撒布の前後による純光合成速度の比較
を示すグラフである。FIG. 8 is a graph showing a comparison of a net photosynthetic rate before and after ozone water spraying.
【図9】オゾン水撒布の前後による純光合成速度の比較
を示す他のグラフである。FIG. 9 is another graph showing a comparison of net photosynthetic rates before and after ozone water spraying.
1 オゾン水製造装置 2 オゾン水タンク 3 アルカリ水タンク 4 植物栽培ハウス 5 陽極水(オゾン水)排出管 5a 陽極水(オゾン水)撒布配管 6 陰極水(アルカリ水)排出管 6a 陰極水(アルカリ水)撒布配管 7 オゾン水撒布ノズル 8 陰極水(アルカリ水)撒布ノズル 11 軟水化装置 40 車両 41 発電装置 42 原料水タンク DESCRIPTION OF SYMBOLS 1 Ozone water production apparatus 2 Ozone water tank 3 Alkaline water tank 4 Plant cultivation house 5 Anode water (ozone water) discharge pipe 5a Anode water (ozone water) distribution pipe 6 Cathode water (alkali water) discharge pipe 6a Cathode water (alkali water) ) Spraying pipe 7 Ozone water spraying nozzle 8 Cathode water (alkaline water) spraying nozzle 11 Water softener 40 Vehicle 41 Power generator 42 Raw material water tank
─────────────────────────────────────────────────────
────────────────────────────────────────────────── ───
【手続補正書】[Procedure amendment]
【提出日】平成12年9月12日(2000.9.1
2)[Submission date] September 12, 2000 (2009.1.
2)
【手続補正1】[Procedure amendment 1]
【補正対象書類名】明細書[Document name to be amended] Statement
【補正対象項目名】特許請求の範囲[Correction target item name] Claims
【補正方法】変更[Correction method] Change
【補正内容】[Correction contents]
【特許請求の範囲】[Claims]
【請求項6】 前記電気分解法に使用する原料水が、ア
ルカリ金属型イオン交換樹脂によって軟水処理された軟
水であり、該軟水の電気分解法の結果陰極側に生成した
アルカリ水を前記植物の根元部又はその近傍に撒布する
請求項5に記載の植物の病害防除方法 6. A raw water to be used in the electrolysis method, a soft water which has been softened processed by alkali metal ion exchange resin, the electrolysis of soft water results in the alkaline water produced on the cathode side the plant root portion or disease control method of the plant according to claim 5, sprayed near the
【請求項7】 オゾン水を用いた植物の病害防除装置で
あって、水の電気分解法によって陽極側にオゾン水を生
成するオゾン水製造装置(1)と、 該電解式オゾン水製造装置(1)の陽極側オゾン水排出
管(5)に接続されて前記植物の地上部に前記オゾン水
を撒布するための撒布ノズル(7)を有するオゾン水撒
布配管(5a)と、 前記電解式オゾン水製造装置(1)の陰極水排出管
(6)に接続され、前記植物の根元部又はその近傍に陰
極水を撒布するための撒布ノズル(8)を有する陰極水
撒布配管(6a)とを備えてなる事を特徴とする植物の
病害防除装置 7. An apparatus for controlling plant diseases using ozone water, comprising: an ozone water production apparatus (1) for producing ozone water on the anode side by electrolysis of water; and an electrolytic ozone water production apparatus (10). 1) anode ozone water discharge <br/> pipe with (connected to 5) ozone water spraying pipe having a spraying nozzle (7) for spraying the ozone water on the ground portion of the plant (5a), A cathode water spray pipe (8) connected to a cathode water discharge pipe (6) of the electrolytic ozone water producing device (1) and having a spray nozzle (8) for spraying cathode water at or near the root of the plant; 6a), a plant disease control apparatus characterized by comprising:
【請求項8】 前記陽極側オゾン水排出管(5)から送
給されるオゾン水を貯蔵するオゾン水タンク(2)を備
え、前記オゾン水撒布配管(5a)はポンプ(P1)を
介して該オゾン水タンク(2)に接続されてなる請求項
7に記載の植物の病害防除装置 8. comprising ozone water tank for storing the ozone water fed from the anode side ozone water discharge pipe (5) (2), the ozone water spraying pipe (5a) via a pump (P1) The ozone water tank (2) is connected to the tank.
The plant disease control apparatus according to 7 above.
【請求項9】 前記オゾン水タンク(2)は密閉構造或
いは圧力保持可能なタンクである請求項8に記載の植物
の病害防除装置 Wherein said ozone water tank (2) is disease control apparatus of the plant of claim 8, wherein the sealed structure or pressure capable of holding tank
【請求項10】 前記電解式オゾン水製造装置(1)に
供給する原料水を軟水化処理するためのアルカリ金属型
イオン交換樹脂を用いた軟水化装置(11)を備え、前
記電解式オゾン水製造装置(1)の陰極側にはアルカリ
水を生成する様になし、前記陰極水撒布配管(6a)か
らはアルカリ水が撒布される様にしてなる請求項7乃至
9のいずれかに記載の植物の病害防除装置 Wherein said comprising a water softener using an alkali metal ion exchange resin for treating softening raw water to be supplied to the electrolytic ozone water production apparatus (1) (11), the electrolytic ozone water No so as to produce an alkaline water on the cathode side of the manufacturing apparatus (1), the composed in the manner being sprayed alkali water from the cathode water spraying pipe (6a) according to claim 7 or
9. The plant disease control apparatus according to any one of 9 above.
【請求項11】 前記陰極側排水管(6)から送給され
るアルカリ水を貯蔵するアルカリ水タンク(3)を備
え、前記陰極水撒布配管(6a)はポンプ(P2)を介
して該アルカリ水タンク(3)に接続されてなる請求項
10に記載の植物の病害防除装置 11. The through with alkaline water tank for storing alkaline water fed from the cathode side drain pipe (6) (3), said cathode water spraying pipe (6a) is a pump (P2) alkali Claims connected to a water tank (3)
The plant disease control apparatus according to 10 ,
【請求項12】 原料水タンク(43)と、 該原料水タンク(43)から供給される原料水を電気分
解してオゾン水を生成する電解式オゾン水製造装置
(1)と、 該電解式オゾン水製造装置に必要な電力を供給する発電
装置(41)と、を車両に搭載すると共に、 前記電解式オゾン水製造装置(1)には、オゾン水を排
出する陽極側排水ノズル(1a)と、陰極水を排出する
陰極水排水ノズル(1b)とが形成され、夫々に可撓性
ホースを接続して前記オゾン水及び陰極水を所定場所に
撒布可能に構成してなる事を特徴とするオゾン水撒布装
置 12. A raw water tank (43); an electrolytic ozone water producing apparatus (1) for electrolyzing raw water supplied from the raw water tank (43) to generate ozone water; A power generator (41) for supplying necessary power to the ozone water producing apparatus is mounted on a vehicle, and the electrolytic ozone water producing apparatus (1) has an anode-side drain nozzle (1a) for discharging ozone water. And discharge the cathode water
A cathode water drain nozzle (1b) is formed, and a flexible hose is connected to each of the nozzles so that the ozone water and the cathode water can be sprayed at a predetermined location.
【請求項13】 前記原料水タンク(43)と前記電解
式オゾン水製造装置(1)との間に前記原料水を軟水化
処理する軟水化装置(42)が配置されている請求項1
2に記載のオゾン水撒布装置 13. The method of claim wherein the raw water softening device for processing soften (42) is arranged between the raw water tank (43) and the electrolytic ozone water production apparatus (1) 1
Ozone water spraying device according to 2
【請求項14】 前記軟水化装置(42)が、アルカリ
金属型イオン交換樹脂を用いるものであり、前記電解式
オゾン水製造装置(1)の陰極側排水ノズル(1b)か
らアルカリ水が排出される様にしてなる請求項13に記
載のオゾン水撒布装置 14. The water softening device (42) uses an alkali metal ion exchange resin, and alkaline water is discharged from a cathode side drain nozzle (1b) of the electrolytic ozone water producing device (1). 14. The apparatus for spraying ozone water according to claim 13 , wherein
【手続補正2】[Procedure amendment 2]
【補正対象書類名】明細書[Document name to be amended] Statement
【補正対象項目名】0009[Correction target item name] 0009
【補正方法】変更[Correction method] Change
【補正内容】[Correction contents]
【0009】第二の特徴は、前記オゾン水を弱酸性水と
なすものであり、これにより、貯留中及び配管内輸送中
におけるオゾン水中のオゾンの分解速度を抑えてオゾン
の効果持続時間を長くし、オゾン水撒布の実効を高める
点にある。この場合のオゾン水のpHは、3以上且つ7
未満が好ましく、水の電解式オゾン水製造法では、陽極
に弱酸性のオゾン水が生成されるので、これをそのまま
用いる方式もあるが、更に酸を添加してpH調整を行う
方式も一般的である。この場合に使用する酸としては、
植物の成育中は希塩酸,希硫酸等の強酸の希釈水溶液を
用いることができ、可食部である野菜や果実の収穫前に
は、酢酸,クエン酸,リンゴ酸等の弱酸を添加して前記
pH調整を行うのが好ましい。[0009] The second feature is that the ozone water is made into a weakly acidic water, whereby the rate of decomposition of ozone in the ozone water during storage and transportation during piping is suppressed, and the duration of the ozone effect is extended. In addition, the point is to enhance the effectiveness of ozone water spraying. In this case, the pH of the ozone water is 3 or more and 7
Less than the preferred , in the water electrolytic ozone water production method, the anode
Since slightly acidic ozone water is generated,
There is a method to use, but further adjust the pH by adding acid
The method is also common. The acid used in this case is
During the growth of the plant, a diluted aqueous solution of a strong acid such as dilute hydrochloric acid or dilute sulfuric acid can be used. Before harvesting vegetables or fruits that are edible parts, a weak acid such as acetic acid, citric acid, or malic acid is added. It is preferable to adjust the pH.
【手続補正3】[Procedure amendment 3]
【補正対象書類名】明細書[Document name to be amended] Statement
【補正対象項目名】0010[Correction target item name] 0010
【補正方法】変更[Correction method] Change
【補正内容】[Correction contents]
【0010】オゾン水としては、高濃度オゾン水が得易
い水の電気分解法により陽極側に生成させたオゾン水を
用いる。この場合に、電解のための原料水として、アル
カリ金属型イオン交換樹脂を用いて軟水化処理した軟水
を使用すると、陰極側にアルカリ水が生成するので、こ
のアルカリ水を、灌水として前記植物の根元又はその近
傍に撒布する事もできる。これにより、植物の生理機能
の強化と共に該植物の根元やその近傍の地表面に落下し
た前記弱酸性のオゾン水を中和してオゾン水中のオゾン
の分解を促進させる効果もある。As the ozone water , ozone water generated on the anode side by an electrolysis method of water in which high-concentration ozone water is easily obtained can be used.
Used . In this case, as raw water for electrolysis, using soft water treated water softening using an alkali metal-type ion exchange resins Then, since alkaline water is produced on the cathode side, the alkaline water, the plants as Irrigation It can also be sprayed at the root or in the vicinity thereof. This has the effect of strengthening the physiological function of the plant and neutralizing the weakly acidic ozone water that has fallen to the root of the plant or in the vicinity of the ground surface, thereby promoting the decomposition of ozone in the ozone water.
【手続補正4】[Procedure amendment 4]
【補正対象書類名】明細書[Document name to be amended] Statement
【補正対象項目名】0011[Correction target item name] 0011
【補正方法】変更[Correction method] Change
【補正内容】[Correction contents]
【0011】更に、上記植物の病害防除方法を実施する
ための好ましい装置としては、前記水の電気分解法によ
って陽極側にオゾン水を生成するオゾン水製造装置にお
けるオゾン水を排出する陽極側オゾン水排出管には、植
物の地上部にオゾン水を撒布するための撒布ノズルを有
するオゾン水撒布配管を接続し、一方、陰極水排出管に
は、前記植物の根元部又はその近傍に陰極水を撒布する
ための撒布ノズルを有する陰極水撒布配管を接続したも
のを基本とし、この変形例としては、前記オゾン水をオ
ゾン水タンクに貯蔵し、該タンクからポンプを経て前記
オゾン水撒布配管にオゾン水を供給する様にしたものが
あり、この場合のオゾン水タンクは、オゾン水の自然分
解速度を抑制する観点から、密閉構造のタンクであるの
が好ましい。Furthermore, as a preferred apparatus for carrying out the disease control method of the plant, the anode side ozone water for discharging the ozone water in the ozone water production apparatus for producing ozone water to the anode side by the electrolysis of the water The discharge pipe is connected with an ozone water spray pipe having a spray nozzle for spraying ozone water on the above-ground part of the plant, while the cathode water discharge pipe is provided with cathode water at or near the root of the plant. As a modification example, the ozone water is stored in an ozone water tank, and the ozone water is supplied to the ozone water distribution pipe via a pump from the tank by connecting a cathode water spray pipe having a spray nozzle for spraying. In some cases, water is supplied. In this case, the ozone water tank is preferably a tank having a closed structure from the viewpoint of suppressing the natural decomposition rate of ozone water.
【手続補正5】[Procedure amendment 5]
【補正対象書類名】明細書[Document name to be amended] Statement
【補正対象項目名】0014[Correction target item name] 0014
【補正方法】変更[Correction method] Change
【補正内容】[Correction contents]
【0014】[0014]
【発明の実施の形態】以下、本発明について詳細に説明
する。図1は、本発明に係る植物の病害防除方法を実施
するための装置の一例を示す概念図であり、オゾン水製
造装置1として、水の電気分解方式によるオゾン水製造
装置を示している。同図において、水道水等の適宜の原
水を配管10からバルブV1を経て軟質化装置11に供
給し、ここで軟水化処理された原料水を、前記電解式オ
ゾン水製造装置1に供給する。該装置1内では、陽極側
に供給された原料水は、陽極側オゾン水排出管5からオ
ゾン水が排出され、バルブV2を経てオゾン水撒布配管
5aに送給される。同様に陰極側に供給された原料水
は、陰極側排水管6からアルカリ性の陰極水としてバル
ブV3を経て陰極水撒布配管6aに送給される。BEST MODE FOR CARRYING OUT THE INVENTION Hereinafter, the present invention will be described in detail. Figure 1 is a conceptual diagram illustrating an example of an apparatus for carrying out the disease control method of the plant according to the present invention, as the ozone water production apparatus 1, shows the ozone water production apparatus by electrolysis method water . In the figure, appropriate raw water such as tap water is supplied from a pipe 10 to a softening device 11 via a valve V1, and raw water subjected to softening treatment is supplied to the electrolytic ozone water producing device 1. In the apparatus 1, the raw water supplied to the anode side is discharged with ozone water from the ozone water discharge pipe 5 on the anode side, and is supplied to the ozone water spray pipe 5a via the valve V2. Similarly, the raw water supplied to the cathode side is supplied from the cathode side drain pipe 6 to the cathode water spray pipe 6a as alkaline cathode water via the valve V3.
【手続補正6】[Procedure amendment 6]
【補正対象書類名】明細書[Document name to be amended] Statement
【補正対象項目名】0019[Correction target item name] 0019
【補正方法】変更[Correction method] Change
【補正内容】[Correction contents]
【0019】因みに、前記電解式オゾン水製造装置1に
供給する原料水を軟水化処理するに当り、軟水化装置1
1としては、ナトリウムに代表されるアルカリ金属を用
いたアルカリ金属型イオン交換樹脂を用いる方式と、水
素型イオン交換樹脂を用いる方式とがあり、前者の場合
には、原水中のカルシウムやマグネシウムをアルカリ金
属に置換するものであるので、陰極面には水中に微量に
含まれているナトリウムイオン(Na+ )やカルシウム
イオン(Ca++)等のアルカリ金属イオンやアルカリ土
類金属イオンも集まって濃縮され、陰極側の水をアルカ
リ水となし、前述の水素ガスと共に陰極水排出口29か
らアルカリ水を排出し、前述の配管12を経てアルカリ
水タンク3に送給される事になる。この様に、陰極側に
は、水素ガスと共に水中に微量に含まれているアルカリ
金属イオンやアルカリ土類金属イオン(主としてN
a+ )も濃縮される結果、陰極側の水はpH9〜11或
いはそれ以上のアルカリ水が生成される事が確認されて
いる。一方、後者の場合には、原水中のカルシウムやマ
グネシウムを水素に置換するので、アルカリ水は生成さ
れず、略中性の陰極水が排出される事になる。尚、これ
らイオン交換樹脂の再生処理に当り、前者の場合はナト
リウムイオンを生成する食塩水で再生されるが、後者の
場合には、水素イオンを生成する希塩酸や希硫酸等を使
用するため、これらの酸の保存や酸性排水処理の問題が
生じるので、ナトリウム型(アルカリ金属型)イオン交
換樹脂を用いるのが好ましい方式である。以下は、係る
アルカリ金属型イオン交換樹脂による軟水化装置を用い
て陰極側にアルカリ水を生成する場合の例について説明
する。Incidentally, when the raw water supplied to the electrolytic ozone water producing apparatus 1 is subjected to water softening treatment, the water softening apparatus 1
As 1, there are a method using an alkali metal type ion exchange resin using an alkali metal represented by sodium and a method using a hydrogen type ion exchange resin. In the former case, calcium and magnesium in raw water are removed. Alkali metal ions and alkaline earth metal ions such as sodium ions (Na + ) and calcium ions (Ca ++ ) contained in trace amounts in the water collect on the cathode surface because they are replaced with alkali metals. concentrated, alkaline water and without water on the cathode side, the alkaline water discharged from the cathode water outlet 29 together with the aforementioned hydrogen gas will be fed to the alkaline water tank 3 through the pipe 12 before mentioned. As described above, on the cathode side, alkali metal ions or alkaline earth metal ions (mainly N
It has been confirmed that as a result of concentration of a + ), alkaline water having a pH of 9 to 11 or higher is generated as water on the cathode side. On the other hand, in the latter case, calcium and magnesium in the raw water are replaced with hydrogen, so that no alkaline water is generated and almost neutral cathode water is discharged. In the regeneration treatment of these ion exchange resins, the former is regenerated with a saline solution that generates sodium ions.In the latter case, dilute hydrochloric acid or dilute sulfuric acid that generates hydrogen ions is used. The use of a sodium-type (alkali metal-type) ion-exchange resin is a preferable method because problems such as preservation of these acids and treatment of acidic wastewater occur. Hereinafter, an example in which alkaline water is generated on the cathode side using the water softening device using such an alkali metal ion exchange resin will be described.
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI テーマコート゛(参考) A01G 25/09 A01G 25/09 C 4H011 A01M 1/00 A01M 1/00 Z 4K021 7/00 7/00 D A01N 25/02 A01N 25/02 B05B 1/02 B05B 1/02 C02F 1/46 C02F 1/46 Z C25B 1/13 C25B 1/00 F Fターム(参考) 2B022 AA01 DA19 EA10 2B029 AA02 BB06 GA06 MA10 XA03 2B121 AA20 CB02 CB13 CB23 CB33 CB42 CB47 CB61 CC37 EA12 EA21 FA16 4D061 DB01 EA02 EB01 EB04 ED20 4F033 AA06 AA07 BA03 BA04 CA01 DA05 EA06 4H011 AA01 BA01 BB18 BC06 BC18 DA13 DD03 4K021 AA01 AA09 AB15 BA02 BB02 BC01 CA05 CA08 CA09 CA15 DB31 DB53 DC07 ──────────────────────────────────────────────────続 き Continued on the front page (51) Int.Cl. 7 Identification code FI Theme coat ゛ (Reference) A01G 25/09 A01G 25/09 C 4H011 A01M 1/00 A01M 1/00 Z 4K021 7/00 7/00 D A01N 25/02 A01N 25/02 B05B 1/02 B05B 1/02 C02F 1/46 C02F 1/46 Z C25B 1/13 C25B 1/00 F F term (reference) 2B022 AA01 DA19 EA10 2B029 AA02 BB06 GA06 MA10 XA03 2B121 AA20 CB02 CB13 CB23 CB33 CB42 CB47 CB61 CC37 EA12 EA21 FA16 4D061 DB01 EA02 EB01 EB04 ED20 4F033 AA06 AA07 BA03 BA04 CA01 DA05 EA06 4H011 AA01 BA01 BB18 BC06 BC18 DA13 DD01 ACO3 DBA13A03
Claims (15)
おいて、オゾン水濃度が30ppm以下で弱酸性のオゾ
ン水を植物の地上部に撒布する事を特徴とする植物の病
害防除方法1. A method for controlling plant diseases using ozone water, wherein a weakly acidic ozone water having an ozone water concentration of 30 ppm or less is sprayed on the aerial part of the plant.
ある請求項1に記載の植物の病害防除方法2. The method for controlling plant diseases according to claim 1, wherein the ozone water concentration is 2 to 20 ppm.
の弱酸性である請求項1又は2に記載の植物の病害防除
方法3. The method for controlling plant diseases according to claim 1, wherein the pH of the ozone water is 3 or more and less than 7 and weakly acidic.
強酸の希釈水を添加して前記pH調整を行い、得られた
弱酸性のオゾン水を、成育中の植物に撒布する請求項3
に記載の植物の病害防除方法4. The pH adjustment is performed by adding diluted water of a strong acid such as dilute hydrochloric acid or dilute sulfuric acid to the ozone water, and the obtained weakly acidic ozone water is sprayed on growing plants.
Method for controlling plant diseases described in
ンゴ酸等の弱酸を添加して前記pH調整を行い、得られ
た弱酸性のオゾン水を、植物に可食部に撒布する請求項
3に記載の植物の病害防除方法5. The pH adjustment is performed by adding a weak acid such as acetic acid, citric acid or malic acid to the ozone water, and the obtained weakly acidic ozone water is sprayed on the edible portion of the plant. 3. The method for controlling plant diseases according to 3.
陽極側に生成させたオゾン水である請求項1乃至5のい
ずれかに記載の植物の病害防除方法6. The method for controlling plant diseases according to claim 1, wherein the ozone water is ozone water generated on the anode side by a water electrolysis method.
ルカリ金属型イオン交換樹脂によって軟水処理された軟
水であり、該軟水の電気分解法の結果陰極側に生成した
アルカリ水を前記植物の根元又はその近傍に撒布する請
求項6に記載の植物の病害防除方法7. The raw water used in the electrolysis method is soft water that has been softened with an alkali metal ion exchange resin, and the alkaline water generated on the cathode side as a result of the soft water electrolysis method is used for the plant. The method for controlling plant diseases according to claim 6, wherein the method is sprayed at or near the root.
あって、 水の電気分解法によって陽極側にオゾン水を生成するオ
ゾン水製造装置(1)と、 該電解式オゾン水製造装置(1)の陽極側排水管(5)
に接続され、前記植物の地上部に前記オゾン水を撒布す
るための撒布ノズル(7)を有するオゾン水撒布配管
(5a)と、 前記電解式オゾン水製造装置(1)の陰極側排水管
(6)に接続され、前記植物の根元部又はその近傍に陰
極水を撒布するための撒布ノズル(8)を有する陰極水
撒布配管(6a)とを備えてなる事を特徴とする植物の
病害防除装置8. A plant disease control apparatus using ozone water, comprising: an ozone water production apparatus (1) for producing ozone water on the anode side by a water electrolysis method; and an electrolytic ozone water production apparatus (8). 1) Anode side drain pipe (5)
An ozone water spray pipe (5a) having a spray nozzle (7) for spraying the ozone water on the above-ground part of the plant; and a cathode-side drain pipe of the electrolytic ozone water production device (1). 6) a cathodic water spray pipe (6a) having a spray nozzle (8) for spraying cathodic water at or near the root of the plant, the plant disease control comprising: apparatus
オゾン水を貯蔵するオゾン水タンク(2)を備え、前記
オゾン水撒布配管(5a)はポンプ(P1)を介して該
オゾン水タンク(2)に接続されてなる請求項8に記載
の植物の病害防除装置9. An ozone water tank (2) for storing ozone water supplied from the anode side drain pipe (5), and the ozone water spray pipe (5a) is provided with a pump (P1). The plant disease control apparatus according to claim 8, which is connected to a water tank (2).
或いは圧力保持可能なタンクである請求項9に記載の植
物の病害防除装置10. The plant disease control apparatus according to claim 9, wherein the ozone water tank (2) is a closed structure or a tank capable of holding pressure.
供給する原料水を軟水化処理するためのアルカリ金属型
イオン交換樹脂を用いた軟水化装置(11)を備え、前
記電解式オゾン水製造装置(1)の陰極側にはアルカリ
水を生成する様になし、前記陰極水撒布配管(6a)か
らはアルカリ水が撒布される様にしてなる請求項8乃至
10のいずれかに記載の植物の病害防除装置11. A water softening device (11) using an alkali metal ion exchange resin for softening raw water supplied to the electrolytic ozone water producing device (1), wherein the electrolytic ozone water is provided. The alkaline water is generated on the cathode side of the manufacturing apparatus (1), and the alkaline water is sprayed from the cathode water spray pipe (6a). Plant disease control equipment
るアルカリ水を貯蔵するアルカリ水タンク(3)を備
え、前記陰極水撒布配管(6a)はポンプ(P2)を介
して該アルカリ水タンク(3)に接続されてなる請求項
11に記載の植物の病害防除装置12. An alkaline water tank (3) for storing alkaline water supplied from the cathode side drain pipe (6), and the cathode water spray pipe (6a) is connected to the alkaline water tank via a pump (P2). The plant disease control apparatus according to claim 11, which is connected to a water tank (3).
解してオゾン水を生成する電解式オゾン水製造装置
(1)と、 該電解式オゾン水製造装置に必要な電力を供給する発電
装置(41)と、を車両に搭載すると共に、 前記電解式オゾン水製造装置(1)には、オゾン水を排
出する陽極側排水ノズル(1a)と、陰極側排水ノズル
(1b)とが形成され、夫々に可撓性ホースを接続して
前記オゾン水及び陰極水を所定場所に撒布可能に構成し
てなる事を特徴とするオゾン水撒布装置13. A raw water tank (43); an electrolytic ozone water producing apparatus (1) for electrolyzing raw water supplied from the raw water tank (43) to generate ozone water; A power generator (41) for supplying necessary power to the ozone water producing apparatus is mounted on a vehicle, and the electrolytic ozone water producing apparatus (1) has an anode-side drain nozzle (1a) for discharging ozone water. And a cathode-side drain nozzle (1b) are formed, each of which is connected to a flexible hose so that the ozone water and the cathode water can be sprayed to a predetermined location.
式オゾン水製造装置(1)との間に前記原料水を軟水化
処理する軟水化装置(42)が配置されている請求項1
3に記載のオゾン水撒布装置14. A water softening device (42) for softening the raw water is disposed between the raw water tank (43) and the electrolytic ozone water producing device (1).
Ozone water spraying device according to 3
金属型イオン交換樹脂を用いるものであり、前記電解式
オゾン水製造装置(1)の陰極側排水ノズル(1b)か
らアルカリ水が排出される様にしてなる請求項14に記
載のオゾン水撒布装置15. The water softening device (42) uses an alkali metal ion exchange resin, and alkaline water is discharged from a cathode side drain nozzle (1b) of the electrolytic ozone water producing device (1). 15. The apparatus for spraying ozone water according to claim 14, wherein
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