JPH0775775A - Treatment of waste liquid to remove agricultural chemicals - Google Patents

Treatment of waste liquid to remove agricultural chemicals

Info

Publication number
JPH0775775A
JPH0775775A JP5289913A JP28991393A JPH0775775A JP H0775775 A JPH0775775 A JP H0775775A JP 5289913 A JP5289913 A JP 5289913A JP 28991393 A JP28991393 A JP 28991393A JP H0775775 A JPH0775775 A JP H0775775A
Authority
JP
Japan
Prior art keywords
waste liquid
activated carbon
treatment method
flocs
waste
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.)
Granted
Application number
JP5289913A
Other languages
Japanese (ja)
Other versions
JP3069821B2 (en
Inventor
Kenji Muramoto
憲司 村本
Akira Suzuki
昭 鈴木
Takahiro Hattori
隆宏 服部
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Nihon Nohyaku Co Ltd
Original Assignee
Nihon Nohyaku Co Ltd
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Nihon Nohyaku Co Ltd filed Critical Nihon Nohyaku Co Ltd
Priority to JP5289913A priority Critical patent/JP3069821B2/en
Publication of JPH0775775A publication Critical patent/JPH0775775A/en
Application granted granted Critical
Publication of JP3069821B2 publication Critical patent/JP3069821B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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  • Treatment Of Water By Ion Exchange (AREA)
  • Removal Of Specific Substances (AREA)
  • Water Treatment By Sorption (AREA)
  • Separation Of Suspended Particles By Flocculating Agents (AREA)

Abstract

PURPOSE:To obviate the generation of environmental pollution even if a treated liquid is released into natural water systems by efficiently removing the agricultural chemicals in waste liquids, such as waste disinfecting liquids for rice seeds, bulbs, etc., waste liquids of seed presoaking for hastening of germination, liquid remaining in tanks of agricultural chemical spraying machines and waste washing liquids of spraying appliances. CONSTITUTION:This method for treatment of the waste liquid comprises removing the agricultural chemicals by adding a powder active carbon and inorg. and/or org. flocculating agent to the waste liquid contg. one or >=2 kinds of the agricultural chemicals in a dispersed and/or dissolved state to form flocs, passing the filtrate obtd. after the formed flocs are filtered through a granular active carbon column and further, passing the flocs through an anion exchange resin column.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は,種籾や球根等の消毒廃
液,催芽浸種廃液,農薬散布機のタンク内残液,散布器
具洗浄廃液等を,自然の水系に流しても環境汚染を引き
起こさせないようにする農薬等の有害物質を含む廃液の
処理方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention does not cause environmental pollution even when a disinfecting waste liquid such as seed paddy or bulbs, a germination soaking waste liquid, a residual liquid in a tank of a pesticide sprayer, a spraying device cleaning waste liquid, etc. is flowed into a natural water system. The present invention relates to a method for treating waste liquid containing harmful substances such as pesticides.

【0002】[0002]

【従来の技術】近年,食料生産に果たす農薬の役割は益
々その重要度を増している。その一方,農薬の使用者へ
の安全性,環境への影響,作物残留等の問題が強く認識
されるようになってきている。このために,安全性の高
い農薬の開発や効率的な剤形および施用法の開発等が盛
んに行われており,それぞれ大きな進展がみられる。更
に最近では,農薬の包装容器や廃液の処理にも多大の注
意が払われるようになっている。
2. Description of the Related Art In recent years, the role of pesticides in food production has become increasingly important. On the other hand, issues such as the safety of pesticides to users, the impact on the environment, and crop residues have been strongly recognized. For this reason, development of highly safe agricultural chemicals and development of efficient dosage forms and application methods have been actively carried out, and significant progress has been made in each. Furthermore, much attention has recently been paid to the treatment of agricultural chemical packaging containers and waste liquids.

【0003】この農薬を含む廃液処理の問題を解決する
ために種々の試みがなされている。例えば,チウラム
剤を含む農薬廃液を,凝集処理後に活性炭処理を行う方
法(特公昭62─24156号);水中に乳化あるい
は,溶解している農薬原体を活性炭に吸着後その懸濁液
を凝集処理する方法(特開平4─161266号);等
が開示されている。しかし,これらの方法は実用場面で
不充分な点があり,更に改良が必要である。即ちの方
法では,凝集濾過後の濾液に含まれる農薬原体は微量
(チウラムの水溶解度は,30ppm;CIPACハン
ドブック)であることが必須であり,水溶解度が高い農
薬原体を含む廃液処理には応用できない。
Various attempts have been made to solve the problem of waste liquid treatment containing this pesticide. For example, a method in which a pesticide waste solution containing a thiuram agent is subjected to a coagulation treatment and then an activated carbon treatment (Japanese Patent Publication No. 62-24156); A method of processing (Japanese Patent Laid-Open No. 4-161266); etc. are disclosed. However, these methods have insufficient points in practical use, and further improvement is necessary. In the method, it is essential that the amount of the agricultural chemical substance contained in the filtrate after coagulation filtration is very small (the water solubility of thiuram is 30 ppm; CIPAC Handbook), and the waste liquid treatment containing the agricultural chemical substance with high water solubility is essential. Is not applicable.

【0004】又,の方法は,水中に乳化あるいは溶解
している農薬原体を活性炭に吸着させた後,凝集濾過す
ることにより上記の問題を回避しようとするものである
が,水溶解度の高い農薬を高濃度に含む廃液の場合に多
量の活性炭を必要とする。その結果,凝集フロックの容
積が増大し,濾過操作に長時間及び/又は過大な設備が
必要となる。また,上水の処理に,活性炭吸着と凝集濾
過を組み合わせた方法を用いている例はよく知られてい
るが,この場合臭気除去を主たる目的として極微量の溶
質が対象とされており,処理設備も極めて大規模なもの
である。
The method (1) attempts to avoid the above problems by adsorbing a pesticide raw material, which is emulsified or dissolved in water, on activated carbon and then performing coagulation filtration, but it has high water solubility. A large amount of activated carbon is required in the case of waste liquid containing a high concentration of pesticides. As a result, the volume of the flocculation flocs increases, and the filtration operation requires a long time and / or excessive equipment. In addition, it is well known that a method combining activated carbon adsorption and coagulation filtration is used for the treatment of tap water, but in this case, an extremely small amount of solute is targeted mainly for the purpose of removing odor. The equipment is also very large.

【0005】[0005]

【発明が解決しようとする課題】近年の高まる環境問題
に対し,種籾や球根等の消毒廃液,催芽浸種廃液,農薬
散布機のタンク内残液,散布器具洗浄廃液等を,自然の
水系に流しても環境汚染を引き起こさせないようにする
ための農薬を含む廃液の処理方法の開発が強く望まれて
いる。しかし,簡便で経済的な農薬等の有害物質を除去
する廃液の処理方法は得られていない。
In response to increasing environmental problems in recent years, disinfectant waste liquid such as seed paddy and bulbs, germination soaking waste liquid, residual liquid in tank of pesticide sprayer, spraying device cleaning waste liquid, etc. are poured into a natural water system. However, it is strongly desired to develop a method for treating waste liquid containing agricultural chemicals so as not to cause environmental pollution. However, a simple and economical method for treating waste liquid to remove harmful substances such as agricultural chemicals has not been obtained.

【0006】[0006]

【課題を解決するための手段】本発明者等は,上記問題
点を解決すべく鋭意研究した結果,従来の公知技術から
は予想できない優れた効果を発揮し,簡便で経済的な農
薬等の有害物質を除去することができる廃液の処理方法
を見出した。
Means for Solving the Problems As a result of intensive studies to solve the above problems, the inventors of the present invention exerted an excellent effect that cannot be predicted from the conventional known techniques, and provided a simple and economical pesticide. We have found a waste liquid treatment method that can remove harmful substances.

【0007】従来から,水中に溶解している有機物を活
性炭に吸着させて除去する方法や,水中に分散している
物質を凝集濾過して除去する方法は,公知の手段であ
る。一方,農薬等の有害物質を除去する廃液の処理は,
種籾や球根等の消毒廃液,催芽浸種廃液,農薬散布機の
タンク内残液,散布器具洗浄廃液等が対象となる。更に
これらに含まれる農薬等の有害物質は,水に不溶または
難溶性な物質から水溶性の物質まで広い範囲の物性を有
しており,通常100ppm以上の濃度で含まれている。これ
らの農薬等の有害物質を廃液から除去する場合,水に不
溶または難溶性な物質は僅かに溶解しているだけで大部
分が水中に懸濁分散している。従って,凝集濾過によっ
て大部分の有害物質が容易に除去でき,溶解している部
分は少量の活性炭で効率よく吸着除去が行える。これに
対して,水溶解度が高い(常温で100ppm以上)物質は,
高濃度で溶解しているため凝集濾過では除去できず,多
量の活性炭を用いて吸着除去する必要がある。又,種籾
や球根等の消毒には,農薬処理済の種籾等と未処理の種
籾等を区別するためのマーカーとして,青色1号等の色
素処理がされているが,この色素を除去するためには,
多量の活性炭を用いて吸着除去する必要がある。
Conventionally, a method of adsorbing an organic substance dissolved in water onto activated carbon to remove it, and a method of coagulating and filtering a substance dispersed in water to remove are known means. On the other hand, the treatment of waste liquid that removes harmful substances such as pesticides is
The target is disinfecting waste liquid such as seed paddy and bulb, germination soaking waste liquid, residual liquid in tank of pesticide sprayer, spraying device cleaning waste liquid, etc. Further, harmful substances such as pesticides contained in these have a wide range of physical properties, from substances that are insoluble or sparingly soluble in water to substances that are water-soluble, and are usually contained in concentrations of 100 ppm or more. When these harmful substances such as pesticides are removed from the waste liquid, most of the substances that are insoluble or sparingly soluble in water are slightly dissolved and suspended and dispersed in water. Therefore, most of the harmful substances can be easily removed by coagulation filtration, and the dissolved portion can be efficiently adsorbed and removed with a small amount of activated carbon. In contrast, substances with high water solubility (100 ppm or more at room temperature)
Since it is dissolved at a high concentration, it cannot be removed by coagulation filtration, and it is necessary to remove it by adsorption using a large amount of activated carbon. In addition, for disinfection of seeds and bulbs, a pigment treatment such as Blue No. 1 is used as a marker to distinguish between seeds that have been treated with pesticides and seeds that have not been treated. Has
It is necessary to remove it by adsorption using a large amount of activated carbon.

【0008】即ち,活性炭への有機物の吸着は主に物理
的吸着であり,有機物の種類によって吸着力が大きく異
なり,一般に疏水的な性質と低濃度の吸着力が大きいと
いうのが活性炭の特性(活性炭,炭素材料学会編,講談
社)である。それ故に,水溶解度の高い物質は,活性炭
の吸着力を低下させる。また高濃度であることは活性炭
吸着に更に不利な条件となる。又,色素の除去には,大
量の粉末活性炭が必要となるため,実用的な処理方法と
はいえない。
That is, the adsorption of organic substances on activated carbon is mainly physical adsorption, and the adsorption power largely differs depending on the type of organic substance. Generally, the hydrophobic property and the low concentration adsorption power are large. Activated carbon, edited by Carbon Society of Japan, Kodansha). Therefore, substances with high water solubility reduce the adsorption power of activated carbon. A high concentration is a further disadvantageous condition for adsorbing activated carbon. In addition, a large amount of powdered activated carbon is required to remove the pigment, which is not a practical treatment method.

【0009】本発明は,農薬等の有害物質を含む廃液に
1%以下,好ましくは0.05%〜0.3%の粉末活性炭を攪
拌下に添加し,次いで無機又は/及び有機の凝集剤を加
えてフロックを形成させる第一段階処理と,濾過により
このフロックを除いた濾液を粒状活性炭カラムに空間速
度20以下好ましくは,空間速度5〜10の流速で通過させ
溶解残存する微量の有害物質を除去する第二段階処理及
び必要により陰イオン交換樹脂塔を通過させ,活性炭塔
で除去できにくい物質,例えば色素等を除去する第三段
階処理からなる廃液処理方法を提供することにある。空
間速度は充填層を通過する流速を表す言葉であり,次式
によって算出される。
According to the present invention, 1% or less, preferably 0.05% to 0.3% of powdered activated carbon is added to a waste liquid containing harmful substances such as agricultural chemicals under stirring, and then an inorganic or / and organic flocculant is added to the flocs. The first step treatment for forming a slag is carried out, and the filtrate from which the flocs are removed is passed through a granular activated carbon column at a space velocity of 20 or less, preferably at a space velocity of 5 to 10 to remove a trace amount of residual harmful substances. It is an object of the present invention to provide a waste liquid treatment method comprising a two-step treatment and, if necessary, passing through an anion-exchange resin tower and removing a substance which is difficult to be removed by an activated carbon tower, for example, a dye, etc. Space velocity is a term that expresses the flow velocity through the packed bed and is calculated by the following equation.

【数1】 活性炭カラムに充填する活性炭は,従来この分野で使用
されている粒状活性炭が使用できる。陰イオン交換樹脂
を併用することにより,活性炭で除去しにくい物質が除
去できるとともに活性炭の使用量を節減することができ
る。陰イオン交換樹脂の寿命は,廃液中の不純物の濃
度,廃液の通水速度に大きく影響する。粒状活性炭処理
した濾液は,空間速度100 以下好ましくは,空間速度5
〜50の流速で通過させ溶解残存する微量の有害物質を除
去する。
[Equation 1] As the activated carbon packed in the activated carbon column, granular activated carbon conventionally used in this field can be used. By using an anion exchange resin together, it is possible to remove substances that are difficult to remove with activated carbon and to reduce the amount of activated carbon used. The life of anion exchange resin greatly affects the concentration of impurities in the waste liquid and the water flow rate of the waste liquid. The filtrate treated with granular activated carbon should have a space velocity of 100 or less, preferably a space velocity of 5 or less.
Pass through at a flow rate of ~ 50 to remove traces of harmful substances that remain dissolved.

【0010】特に,廃液に含まれる農薬等の有害物質の
水溶解度が100ppm以上の場合に本発明の処理方法の有用
性が顕著に発揮される。即ち,第一段階処理において,
1%以下好ましくは0.05〜 0.3%の粉末活性炭に吸着さ
せて水中に溶解している有害物質濃度を低下せしめ,第
二段階処理に使用する粒状活性炭塔の有効作用期間を大
幅に延長することができる。この場合,1%以上の粉末
活性炭の添加は,凝集フロックの量が増大し,濾過を困
難にするとともにスラッジの処理が増大するので,望ま
しくない。
Particularly, the usefulness of the treatment method of the present invention is remarkably exhibited when the water solubility of harmful substances such as pesticides contained in the waste liquid is 100 ppm or more. That is, in the first stage processing,
Adsorbing to 1% or less, preferably 0.05 to 0.3% of powdered activated carbon to reduce the concentration of harmful substances dissolved in water, it is possible to significantly extend the effective action period of the granular activated carbon tower used for the second stage treatment. it can. In this case, the addition of 1% or more of powdered activated carbon is not desirable because it increases the amount of agglomerated flocs, makes filtration difficult and increases sludge treatment.

【0011】凝集フロックの濾過は,凝集フロックの物
性によって濾過性能が大きく異なるが,凝集フロックが
微細であれば,濾布等の目が粗いと凝集フロック物が漏
れ,目が細かければ目詰まりを生じる。自然濾過におい
て使用される濾過材としては,濾布,濾紙,ポリウレタ
ンシート等が挙げられるが,濾布,濾紙等では目詰まり
がし易いため,中でも多孔質のポリウレタンシート,例
えば連続気泡の発泡ポリウレタンシートなどが望まし
い。分離した凝集フロックは,焼却炉で焼却処理するこ
とができる。活性炭に吸着した農薬成分等は活性炭の高
温再生処理により分解できるので,第二段処理としての
活性炭は繰り返し使用可能である。活性炭で除去しにく
い物質の除去に用いる陰イオン交換樹脂は,母体構造と
しては,スチレン系とアクリル系(メタアクリル系)が
あり,合成法によりゲル形,ポーラス形,MR形に分類
される。強塩基性陰イオン交換樹脂は形成される4級塩
の種類によってI型(メチルアミン型)とII型(ジメチ
ルアミン型)に分類される。 本発明で使用される陰イ
オン交換樹脂の具体例としては,例えば米国ローム・ア
ンド・ハース社製のアンバーライトIRA-410 ,アンバー
ライトXT-5007 ,アンバーライトXT-5028 等が挙げられ
る。
Filtration performance of agglomerated flocs varies greatly depending on the physical properties of the agglomerated flocs. If the agglomerated flocs are fine, the agglomerated flocs will leak if the filter cloth or the like is coarse, and if the agglomerated flocs are fine, they will be clogged. Cause Examples of the filter material used in the natural filtration include filter cloth, filter paper, and polyurethane sheet. However, since filter cloth, filter paper and the like are easily clogged, a porous polyurethane sheet, for example, foamed polyurethane with open cells is used. Sheets are preferable. The separated floc can be incinerated in an incinerator. Pesticide components adsorbed on activated carbon can be decomposed by high-temperature regeneration treatment of activated carbon, so activated carbon can be used repeatedly as a second-stage treatment. Anion exchange resins used to remove substances that are difficult to remove with activated carbon have styrene type and acrylic type (methacrylic type) as a matrix structure, and are classified into gel type, porous type and MR type by the synthesis method. Strongly basic anion exchange resins are classified into type I (methylamine type) and type II (dimethylamine type) depending on the type of quaternary salt formed. Specific examples of the anion exchange resin used in the present invention include Amberlite IRA-410, Amberlite XT-5007, and Amberlite XT-5028 manufactured by Rohm and Haas Company, USA.

【0012】本発明を実施する装置としては,例えば図
1〜2に示すような装置が使用される。図1において,
1は第一段階処理を行うための処理槽で,パイプ7を介
して送られてきた廃液はこの処理槽1においてパイプラ
イン8によって薬剤タンク5から供給される粉末活性
炭,凝集剤等と共に攪拌される。4は攪拌装置を示す。
次いで,処理槽1内の上澄み液はパイプ9によってサブ
水槽2に送られ,一方,処理槽1の底部に沈む凝集物を
含む処理廃液は処理槽1の底部からパイプ10を介してサ
ブ水槽2内の濾過水槽3に送られ,ここで凝集物等が除
かれ,上澄み液と合わさってパイプ11を経て第二段階処
理を行うための粒状活性炭を充填した吸着塔6に送ら
れ,該塔6で残りの除去成分が除かれ,清浄な液となっ
てパイプ12によって系外に排出される。図2は図1の濾
過水槽3の代わりにフィルタープレス13と活性炭吸着塔
6の他に更に陰イオン交換樹脂塔15を加えたものであ
る。
As an apparatus for carrying out the present invention, for example, an apparatus as shown in FIGS. In Figure 1,
Reference numeral 1 denotes a treatment tank for performing the first-stage treatment. The waste liquid sent through the pipe 7 is agitated in this treatment tank 1 together with powdered activated carbon, a flocculant, etc. supplied from a chemical tank 5 by a pipeline 8. It Reference numeral 4 represents a stirrer.
Next, the supernatant liquid in the treatment tank 1 is sent to the sub water tank 2 through the pipe 9, while the treatment waste liquid containing the aggregates that sinks to the bottom of the treatment tank 1 is passed from the bottom portion of the treatment tank 1 through the pipe 10 to the sub water tank 2. It is sent to a filtered water tank 3 inside, where aggregates and the like are removed, and it is sent to an adsorption tower 6 filled with granular activated carbon for performing a second stage treatment through a pipe 11 after being combined with the supernatant liquid, and the tower 6 The remaining removal components are removed by and become a clean liquid, which is discharged to the outside of the system by the pipe 12. In FIG. 2, an anion exchange resin tower 15 is added in addition to the filter press 13 and the activated carbon adsorption tower 6 instead of the filtered water tank 3 of FIG.

【0013】[0013]

【実施例】以下に本発明の実施例を示すが,本発明はこ
れらのみに限定されるものではない。
EXAMPLES Examples of the present invention will be shown below, but the present invention is not limited thereto.

【0014】実施例1 ベフラゾエート20%水和剤(水溶解度443ppm)の200 倍
液2L(リットル)に種籾1.5 kgを浸漬し,24時間後種
籾を取り出して浸種廃液を得る。この廃液1Lに粉末活
性炭 0.4gを添加し,1時間攪拌後,ポリ塩化アルミニ
ウム溶液(多木化学(株)製,Al2O3 として10%)を2
g添加し,5%NaOHを加えてpHを7〜8とする。次い
で高分子凝集剤(三洋化成(株)製,サンフロックSW
−210P)を5ppm 添加し,攪拌する。静置後,上澄
み液を粒状活性炭(粒径5〜0.5mm)5gを充填した径
18mmのカラムに流速130ml /hr(空間速度10 1/hr)
で500 ml通過させる。結果を表1に示す。
Example 1 1.5 kg of seed rice was soaked in 2 L (liter) of a 200 times solution of befrazoate 20% wettable powder (water solubility 443 ppm), and after 24 hours, the seed rice was taken out to obtain a steeping waste liquid. 0.4 g of powdered activated carbon was added to 1 L of this waste liquid, and after stirring for 1 hour, polyaluminum chloride solution (Taki Chemical Co., Ltd., 10% as Al 2 O 3 ) was added to 2
g and 5% NaOH to bring the pH to 7-8. Next, polymer flocculant (manufactured by Sanyo Kasei Co., Ltd., Sunflock SW)
Add 5 ppm of -210P) and stir. After standing, the supernatant was loaded on a column with a diameter of 18 mm packed with 5 g of granular activated carbon (particle diameter 5 to 0.5 mm), and the flow rate was 130 ml / hr (space velocity 10 1 / hr).
And pass 500 ml. The results are shown in Table 1.

【0015】実施例2 消毒籾(ベフラゾエート15%乳剤の7.5 倍希釈液及びフ
ェニトロチオン50%乳剤の100 倍希釈液を種子重量の3
%吹き付けし,青色1号で着色)1kgを水2Lに浸漬
し,24時間後種籾を取り出して浸種廃液を得る。この廃
液1Lに粉末活性炭0.25gを添加し,1時間攪拌後,ポ
リ塩化アルミニウム溶液(多木化学(株)製,Al2O3
して10%)を1gを添加し,5%NaOHを加えてpHを7〜
8とする。次いで高分子凝集剤(三洋化成(株)製,サ
ンフロックSW−210P)を5ppm 添加し,攪拌す
る。静置後,上澄液を粒状活性炭(粒径5〜0.5 mm)5
gを充填した径18mmのカラムに空間速度流速130 ml/hr
(空間速度10 1/hr) で2.0L通水する。結果を表1に
示す。
Example 2 Disinfected paddy (befurazoate 15% emulsion 7.5 times diluted and fenitrothion 50% emulsion 100 times diluted 3 times seed weight).
% Spray, and soak 1 kg in Blue No. 1) in 2 L of water, and after 24 hours, remove the seed paddy to obtain a soaking waste liquid. To 1 L of this waste liquid, 0.25 g of powdered activated carbon was added, and after stirring for 1 hour, 1 g of a polyaluminum chloride solution (manufactured by Taki Chemical Co., Ltd., 10% as Al 2 O 3 ) was added, and 5% NaOH was added. pH 7 to
8 Then, 5 ppm of a polymer flocculant (Sanyo Chemical Co., Ltd., Sunfloc SW-210P) is added and stirred. After standing still, the supernatant liquid is treated with granular activated carbon (particle size 5 to 0.5 mm) 5
Space velocity flow rate 130 ml / hr in a column with a diameter of 18 mm filled with g
2.0L of water is passed at a space velocity of 10 1 / hr. The results are shown in Table 1.

【0016】比較例1 実施例1において,粉末活性炭を添加せずに処理を行
う。結果を表1に示す。 比較例2 実施例2において,粉末活性炭を添加せずに処理を行
う。結果を表1に示す。
Comparative Example 1 In Example 1, the treatment is carried out without adding powdered activated carbon. The results are shown in Table 1. Comparative Example 2 In Example 2, the treatment is performed without adding powdered activated carbon. The results are shown in Table 1.

【0017】[0017]

【表1】 [Table 1]

【0018】実施例3 陰イオン交換樹脂に青色1号溶液を100 cc添加して,各
吸着容量を求めた。結果を表2に示す。
Example 3 100 cc of Blue No. 1 solution was added to the anion exchange resin, and each adsorption capacity was determined. The results are shown in Table 2.

【表2】 [Table 2]

【0019】[0019]

【発明の効果】本発明により,種籾や球根等の消毒廃
液,催芽浸種廃液,農薬散布機のタンク内残液,散布器
具洗浄廃液等の廃液中の農薬を効率よく除去することが
でき,処理液を自然の水系に放流しても環境汚染を引き
起こさせないようにすることができる。
EFFECTS OF THE INVENTION According to the present invention, it is possible to efficiently remove pesticides in waste liquid such as disinfectant waste liquid such as seed paddy and bulb, germination soaking waste liquid, residual liquid in tank of pesticide sprayer, spraying equipment cleaning waste liquid, etc. It is possible to prevent environmental pollution even when the liquid is discharged into a natural water system.

【図面の簡単な説明】[Brief description of drawings]

【図1】本発明の実施に使用される装置の一例を示す模
式図である。
FIG. 1 is a schematic view showing an example of an apparatus used for carrying out the present invention.

【図2】本発明の別の実施に使用される装置の一例を示
す模式図である。
FIG. 2 is a schematic view showing an example of an apparatus used for another embodiment of the present invention.

【符号の説明】[Explanation of symbols]

1 第一段階処理用の処理槽 2 サブ水槽 3 濾過水槽 4 攪拌装置 6 活性炭塔 13 フィルタープレス 15 陰イオン交換樹脂塔 1 Treatment tank for first stage treatment 2 Sub water tank 3 Filtration water tank 4 Stirrer 6 Activated carbon tower 13 Filter press 15 Anion exchange resin tower

フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 C02F 9/00 502 P 7446−4D J 7446−4D H 7446−4D Continuation of front page (51) Int.Cl. 6 Identification number Office reference number FI technical display location C02F 9/00 502 P 7446-4D J 7446-4D H 7446-4D

Claims (9)

【特許請求の範囲】[Claims] 【請求項1】 分散及び/又は溶解状態の農薬を1種又
は2種以上含む廃液に,粉末活性炭,無機及び/又は有
機の凝集剤を添加してフロックを形成させ,生成したフ
ロックを濾過した濾液を粒状活性炭塔を通過させて,農
薬を除去する廃液処理方法。
1. A floc is formed by adding powdered activated carbon, an inorganic and / or organic flocculant to a waste liquid containing one or two or more dispersed and / or dissolved pesticides, and the generated flocs are filtered. A waste liquid treatment method that removes pesticides by passing the filtrate through a granular activated carbon tower.
【請求項2】 分散及び/又は溶解状態の農薬を1種又
は2種以上含む廃液に,粉末活性炭,無機及び/又は有
機の凝集剤を添加してフロックを形成させ,生成したフ
ロックを濾過した濾液を粒状活性炭塔,次いで陰イオン
交換樹脂塔を通過させて,農薬を除去する廃液処理方
法。
2. A powdery activated carbon, an inorganic and / or organic flocculant is added to a waste liquid containing one or more kinds of dispersed and / or dissolved pesticides to form flocs, and the generated flocs are filtered. A waste liquid treatment method that removes pesticides by passing the filtrate through a granular activated carbon tower and then an anion exchange resin tower.
【請求項3】 水溶解度が100ppm以上の農薬であ
る請求項第1項又は第2項記載の農薬を除去する廃液処
理方法。
3. The waste liquid treatment method for removing a pesticide according to claim 1 or 2, which is a pesticide having a water solubility of 100 ppm or more.
【請求項4】 廃液に対し粉末活性炭の添加量が,1重
量%以下である請求項第1項又は第2項記載の農薬を除
去する廃液処理方法。
4. The waste liquid treatment method for removing agricultural chemicals according to claim 1 or 2, wherein the amount of powdered activated carbon added to the waste liquid is 1% by weight or less.
【請求項5】 空間速度20以下の流速で,濾液を粒状
活性炭塔を通過させる請求項第1項又は第2項記載の廃
液処理方法。
5. The waste liquid treatment method according to claim 1 or 2, wherein the filtrate is passed through the granular activated carbon tower at a flow velocity of 20 or less in space velocity.
【請求項6】 空間速度100以下の流速で,陰イオン
交換樹脂塔を通過させる請求項第2項記載の廃液処理方
法。
6. The waste liquid treatment method according to claim 2, wherein the liquid is passed through the anion exchange resin tower at a flow velocity of 100 or less in space velocity.
【請求項7】 フロックの濾過にポリウレタンシートを
用いる請求項第1項又は第2項記載の廃液処理方法。
7. The waste liquid treatment method according to claim 1, wherein a polyurethane sheet is used for filtering flocs.
【請求項8】 フィルタープレス法によりフロックを濾
過する請求項第1項又は第2項記載の廃液処理方法。
8. The waste liquid treatment method according to claim 1, wherein flocs are filtered by a filter press method.
【請求項9】 廃液が水溶性の色素を含む液である請求
項第1項又は第2項記載の廃液処理方法。
9. The waste liquid treatment method according to claim 1, wherein the waste liquid is a liquid containing a water-soluble dye.
JP5289913A 1993-07-16 1993-10-26 Wastewater treatment method for removing pesticides Expired - Lifetime JP3069821B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP5289913A JP3069821B2 (en) 1993-07-16 1993-10-26 Wastewater treatment method for removing pesticides

Applications Claiming Priority (3)

Application Number Priority Date Filing Date Title
JP19915093 1993-07-16
JP5-199150 1993-07-16
JP5289913A JP3069821B2 (en) 1993-07-16 1993-10-26 Wastewater treatment method for removing pesticides

Publications (2)

Publication Number Publication Date
JPH0775775A true JPH0775775A (en) 1995-03-20
JP3069821B2 JP3069821B2 (en) 2000-07-24

Family

ID=26511366

Family Applications (1)

Application Number Title Priority Date Filing Date
JP5289913A Expired - Lifetime JP3069821B2 (en) 1993-07-16 1993-10-26 Wastewater treatment method for removing pesticides

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Country Link
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