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JPH0780497A - Treatment of waste liquid - Google Patents

Treatment of waste liquid

Info

Publication number
JPH0780497A
JPH0780497A JP5252281A JP25228193A JPH0780497A JP H0780497 A JPH0780497 A JP H0780497A JP 5252281 A JP5252281 A JP 5252281A JP 25228193 A JP25228193 A JP 25228193A JP H0780497 A JPH0780497 A JP H0780497A
Authority
JP
Japan
Prior art keywords
waste liquid
tank
agent
filtrate
activated carbon
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.)
Pending
Application number
JP5252281A
Other languages
Japanese (ja)
Inventor
Masahide Tomaru
雅英 登丸
Kiyoshi Yamada
清 山田
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.)
Tsurumi Soda Co Ltd
Original Assignee
Tsurumi Soda 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 Tsurumi Soda Co Ltd filed Critical Tsurumi Soda Co Ltd
Priority to JP5252281A priority Critical patent/JPH0780497A/en
Publication of JPH0780497A publication Critical patent/JPH0780497A/en
Pending legal-status Critical Current

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  • Separation Of Suspended Particles By Flocculating Agents (AREA)
  • Water Treatment By Sorption (AREA)

Abstract

PURPOSE:To simplify constitution and control of a device and also to enhance treating efficiency. CONSTITUTION:When a solid-based flocculation treating agent is added to waste liquid of agricultural chemicals in a mixing tank 3 for flocculation and precipitation through a feeder 4, firstly an inorganic flocculant is dissolved and a flocculation nucleus is produced. Mineral contained in waste liquid of agricultural chemicals, a solid component such as mud and the component of agricultural chemicals are stuck to the flocculation nucleus and flocculating particles are produced. A polymer flocculant is stuck to the flocculating particles and a large aggregate is formed. Further the large aggregate is produced efficiently by a settling agent. After the flocculating precipitate produced in such a way is filtrated by a filter 5, it is discarded and filtrate is sent to an adsorption tank 8 packed with activated carbon 82. The component of agricultural chemicals remaining in the filtrate is adsorbed an activated carbon 82 in the adsorption tank 8 and removed and the filtrate is discarded.

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、例えば農薬廃液等の廃
液の処理方法に関する。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for treating waste liquid such as agricultural chemical waste liquid.

【0002】[0002]

【従来の技術】穀物や野菜等の農作物を効率よく収穫す
るために、殺虫剤や殺菌剤、除草剤または発芽及び生長
促進剤等からなる農薬を使用することが一般的である
が、この農薬には毒性のある成分が含まれているため、
処理後の廃液の廃棄には十分な配慮が必要である。
2. Description of the Related Art In order to efficiently harvest crops such as grains and vegetables, it is common to use pesticides composed of insecticides, fungicides, herbicides or germination and growth promoters. Contains toxic ingredients,
Careful consideration must be given to the disposal of waste liquid after processing.

【0003】農薬廃液の廃棄処理の方法としては、例え
ば活性炭による吸着処理法が知られている。この方法は
例えばベノミル及びチウラムを有効成分とするベンレー
トT水和剤20からなる農薬の廃液処理に用いられるも
のであり、水で希釈した農薬廃液に廃液量の2%の量の
活性炭を添加して廃液中のベノミル、チウラムを吸着さ
せた後、廃液量の2.5%の量の液体凝集剤を添加して
浮遊している粒子を凝集、沈降させ、上済み液と凝集沈
殿物に分別して、上澄み液は排水し、凝集沈殿物は乾燥
後焼却するかまたは土壌に埋めて廃棄するというもので
ある。
As a method of disposing of the agricultural chemical waste liquid, for example, an adsorption treatment method using activated carbon is known. This method is used, for example, for treating a pesticide waste solution consisting of Benlate T wettable powder 20 containing benomyl and thiuram as active ingredients, and adding 2% of the amount of the waste solution to the pesticide waste solution diluted with water. After adsorbing benomyl and thiuram in the waste liquid, the liquid coagulant in an amount of 2.5% of the amount of the waste liquid is added to agglomerate and settle the suspended particles, and separate it into a supernatant liquid and an aggregate precipitate. Separately, the supernatant liquid is drained, and the coagulated sediment is dried and then incinerated or buried in soil and discarded.

【0004】またこの方法以外にも、農薬廃液に無機凝
集剤溶液、中和剤溶液、高分子凝集剤溶液を一定間隔を
おいて順次添加し農薬の成分を凝集させた後、この凝集
処理水を固液分離し、ろ過水は農薬吸着塔で農薬を除去
して排水し、固形物は回収して焼却処分する廃液処理方
法も知られている。
In addition to this method, an inorganic coagulant solution, a neutralizing agent solution, and a polymer coagulant solution are sequentially added to an agricultural chemical waste liquid at regular intervals to coagulate the agricultural chemical components, and the coagulated water is then treated. There is also known a waste liquid treatment method in which solids are subjected to solid-liquid separation, filtered water is removed from pesticides in an agrochemical adsorption tower and drained, and solids are collected and incinerated.

【0005】[0005]

【発明が解決しようとする課題】しかしながら上述の活
性炭による吸着処理法には、活性炭が多量に必要であ
り、この活性炭は高価であることからランニングコスト
が高いという問題や、活性炭には農薬の成分が吸着して
いるため再生することができず、廃棄するしかないが、
この廃棄処理に手間がかかりコストが高くなるという問
題があった。
However, the above-mentioned adsorption treatment method using activated carbon requires a large amount of activated carbon, and this activated carbon is expensive, so that the running cost is high, and activated carbon contains agricultural chemical components. Since it is adsorbed, it cannot be regenerated and must be discarded.
There has been a problem that this disposal process requires much labor and costs are high.

【0006】また上述の他の方法には、無機凝集剤溶液
と高分子凝集剤溶液とを同時に添加すると、これらが互
いに反応して、無機凝集剤による凝集核が生じにくく、
効率的な凝集処理を行うことができないので、無機凝集
剤溶液、中和剤溶液、高分子凝集剤溶液を一定間隔をお
いて添加することが必要であるが、このため各溶液を貯
留するタンクやバルブが必要となる他、溶液の供給のタ
イミングを制御することが必要となり、装置が複雑化す
ると共に、処理が煩雑になるという問題があった。
In addition, in the above-mentioned other method, when the inorganic coagulant solution and the polymer coagulant solution are added at the same time, these react with each other, and aggregation nuclei due to the inorganic coagulant hardly occur,
It is necessary to add the inorganic flocculant solution, the neutralizing agent solution, and the polymer flocculant solution at regular intervals because efficient coagulation treatment cannot be performed. In addition to requiring a valve and a valve, it is necessary to control the timing of solution supply, which complicates the apparatus and complicates the processing.

【0007】本発明は、このような事情の下になされた
ものであり、その目的は、装置構成及び制御が簡単であ
ると共に、処理効率の高い廃液処理方法を提供すること
にある。
The present invention has been made under such circumstances, and an object of the present invention is to provide a waste liquid treatment method which has a simple apparatus configuration and control and high treatment efficiency.

【0008】[0008]

【課題を解決するための手段】本発明は、廃液に固体材
料からなる無機凝集剤と、高分子凝集剤と、pH調整剤
と、沈降剤とを含む固体系凝集処理剤を添加し、廃液に
含有する化学的有害成分と固形成分とを凝集させる工程
と、前記凝集処理剤が添加された廃液をろ過する工程
と、この工程により得られたろ過液を活性炭に接触させ
て当該液中に含まれる化学的有害成分を吸着させて除去
する工程と、この工程で得られた処理液を排出する工程
と、からなることを特徴とする。
According to the present invention, a waste liquid is added with a solid-state aggregating agent containing an inorganic aggregating agent made of a solid material, a polymer aggregating agent, a pH adjusting agent, and a sedimenting agent. A step of aggregating the chemically harmful component and the solid component contained in, a step of filtering the waste liquid to which the aggregating treatment agent is added, and the filtrate obtained by this step is brought into contact with activated carbon in the liquid. It is characterized by comprising a step of adsorbing and removing the contained chemically harmful components and a step of discharging the treatment liquid obtained in this step.

【0009】[0009]

【作用】例えば農薬廃液からなる廃液に固体系凝集処理
剤を添加すると、農薬廃液中の固形成分が凝集し、凝集
沈殿物となって沈降すると共に、化学的有害成分である
農薬成分が当該凝集沈殿物に付着する。この凝集沈殿プ
ロセスでは、先ず無機凝集剤が溶解して凝集核となり、
これに固形成分が付着して凝集粒子が生成し、この凝集
粒子にさらに高分子凝集剤が付着しこれがバインダーと
なってさらに大きな凝集体が生成する。また沈降剤の存
在により大きな凝集体が効率よく凝集沈殿する。
[Function] For example, when a solid-based coagulation treatment agent is added to a waste liquid consisting of agricultural chemical waste liquid, the solid components in the agricultural chemical waste liquid are aggregated and settled as aggregate precipitates, and the agricultural chemical components that are chemically harmful components are aggregated. Adhere to the precipitate. In this coagulation-sedimentation process, the inorganic coagulant is first dissolved to form coagulation nuclei,
The solid component adheres to this to form aggregated particles, and the polymer aggregating agent further adheres to the aggregated particles, and this serves as a binder to form larger aggregates. In addition, the presence of the sedimentation agent allows large aggregates to efficiently aggregate and precipitate.

【0010】この凝集沈殿物をろ過して除去した後に、
ろ過液を例えば活性炭の吸着塔を通過させて活性炭と接
触させると、液中に残存する化学的有害成分が活性炭に
吸着し除去される。
After removing the aggregated precipitate by filtration,
When the filtrate is passed through, for example, an activated carbon adsorption tower and brought into contact with activated carbon, the chemically harmful components remaining in the liquid are adsorbed by the activated carbon and removed.

【0011】[0011]

【実施例】以下本発明の実施例について説明する。図1
は本発明の方法を実施するための廃液処理装置の一例を
示す図であり、図中1は廃液例えば農薬廃液を貯留する
ための廃液貯留槽である。この廃液貯留槽1は途中にバ
ルブ12、ポンプ13、調節バルブ14、流量計15、
スタテックミキサー16がこの順番に設けられた供給管
11を介して凝集沈殿用混合槽3に接続されている。ま
た2はカチオン系界面活性剤を貯留するための調整剤槽
であり、この調整剤槽は途中にバルブ22、ポンプ23
が設けられると共に他端側が分岐している供給管21に
より、バルブ24、25を介してスタテックミキサー1
6に接続されている。
EXAMPLES Examples of the present invention will be described below. Figure 1
[FIG. 1] is a diagram showing an example of a waste liquid treatment apparatus for carrying out the method of the present invention, in which 1 is a waste liquid storage tank for storing a waste liquid, for example, an agricultural chemical waste liquid. This waste liquid storage tank 1 has a valve 12, a pump 13, a control valve 14, a flow meter 15,
A static mixer 16 is connected to the coagulation / sedimentation mixing tank 3 via a supply pipe 11 provided in this order. Further, 2 is an adjusting agent tank for storing the cationic surfactant, and this adjusting agent tank has a valve 22 and a pump 23 in the middle thereof.
Is provided and the other end side is branched, and the static mixer 1 is connected via valves 24 and 25.
Connected to 6.

【0012】凝集沈殿用混合槽3は攪拌機31を備える
と共に、凝集処理剤を槽内に供給するためのフィーダー
4が設けられ、底部が逆円錐形状に形成された槽であ
る。この凝集沈殿用混合槽3には下部側壁に電磁弁33
を備えた供給管32が設けられると共に、底部にバルブ
35を備えた供給管34が設けられており、供給管3
2、34は共にろ過装置5に接続されている。
The coagulation-sedimentation mixing tank 3 is a tank having a stirrer 31, a feeder 4 for supplying a coagulation treatment agent into the tank, and a bottom having an inverted conical shape. In this coagulation-sedimentation mixing tank 3, a solenoid valve 33 is provided on the lower side wall.
And a supply pipe 34 having a valve 35 at the bottom thereof.
Both 2 and 34 are connected to the filtration device 5.

【0013】ろ過装置5は例えば多数の孔が形成された
内槽51と、内槽51の外側に設けられた外槽52とか
らなり、内槽51を回転させることにより、液体分を外
槽52へ飛ばして固液分離を行う装置である。このろ過
装置51は供給管53を介してろ過液を一旦貯留するた
めの槽である中間槽6に接続され、中間槽6は途中に電
磁弁62、ポンプ63、電磁弁64がこの順番で設けら
れた供給管61を介してろ過液を貯留するためのろ過液
槽7に接続されている。
The filtering device 5 is composed of, for example, an inner tank 51 having a large number of holes and an outer tank 52 provided outside the inner tank 51. This is a device for skipping to 52 and performing solid-liquid separation. The filtration device 51 is connected via a supply pipe 53 to an intermediate tank 6 which is a tank for temporarily storing the filtrate, and the intermediate tank 6 is provided with a solenoid valve 62, a pump 63, and a solenoid valve 64 in this order in the middle. It is connected to the filtrate tank 7 for storing the filtrate via the supply pipe 61.

【0014】またろ過液槽7は途中に電磁弁72、ポン
プ63、電磁弁73、流量積算計74、調節バルブ7
5、流量計76がこの順番で設けられた供給管71を介
して吸着槽8の下部に設けられたろ過液供給手段81に
接続されている。吸着槽8には活性炭82が充填される
と共に、その表面には多孔質の押え板83が設けられて
おり、また槽の上部側壁には供給管84が接続されてい
る。
The filtrate tank 7 is provided with a solenoid valve 72, a pump 63, a solenoid valve 73, a flow rate integrator 74, and a control valve 7 on the way.
5. The flow meter 76 is connected to the filtrate supply means 81 provided in the lower part of the adsorption tank 8 via the supply pipe 71 provided in this order. The adsorption tank 8 is filled with activated carbon 82, a porous holding plate 83 is provided on the surface thereof, and a supply pipe 84 is connected to the upper side wall of the tank.

【0015】次に上述の農薬廃液処理装置を用いて行わ
れる本発明方法の一例について述べる。廃液貯留槽1に
は、例えばヘルシ−ド、ヘルシ−ドT、ベンレ−ト、ベ
ンレ−トT、トリフミン等の種籾等の種子の消毒に使用
される農薬の処理後の廃液が貯留されており、バルブ1
2を開き、ポンプ13を作動させ、調節バルブ14によ
り流量を制御することにより、スタテックミキサー16
を介して例えば一定量の農薬廃液が連続的に供給管11
により凝集沈殿用混合槽3に供給される。
Next, an example of the method of the present invention which is carried out using the above-mentioned agricultural chemical waste liquid treatment apparatus will be described. The waste liquid storage tank 1 stores the waste liquid after the treatment of pesticides used for disinfecting seeds such as seeds such as Helcede, Helcee T, Benrate, Benrate T, and Trihumin. , Valve 1
2 is opened, the pump 13 is operated, and the flow rate is controlled by the regulating valve 14, whereby the static mixer 16
For example, a fixed amount of agricultural chemical waste liquid is continuously supplied through the pipe 11
Is supplied to the coagulation sedimentation mixing tank 3.

【0016】この際農薬中にアニオン系あるいはノニオ
ン系の界面活性剤が多量に含まれている場合には、バル
ブ22、24を開き、ポンプ23を作動させて、調整剤
槽2から例えばSF−75(三洋化成工業株式会社製)
等のカチオン系界面活性剤がスタテックミキサー16に
供給され、このスタテックミキサ−16により農薬廃液
と界面活性剤とを混合し反応させて、農薬廃液中のアニ
オン系あるいはノニオン系の界面活性剤を不活性化させ
る。
At this time, if the pesticide contains a large amount of anionic or nonionic surfactant, the valves 22 and 24 are opened and the pump 23 is operated to remove SF- from the regulator tank 2, for example. 75 (manufactured by Sanyo Chemical Industry Co., Ltd.)
And the like are supplied to the static mixer 16, and the static mixer 16 mixes and reacts the agricultural chemical waste liquid and the surfactant, and the anionic or nonionic surfactant in the agricultural chemical waste liquid is mixed. Inactivate.

【0017】また凝集沈殿用混合槽3では、供給管11
から供給された農薬廃液にフィーダー4より所定量の例
えば粉末状の凝集処理剤を連続的に添加し、攪拌機31
で混合して凝集処理剤を溶解させた後、電磁弁33を介
してろ過装置5の内槽51へ連続的に送液する。
In the coagulation-sedimentation mixing tank 3, the supply pipe 11
A predetermined amount of, for example, a powdery aggregating treatment agent is continuously added from the feeder 4 to the agricultural chemical waste liquid supplied from the stirrer 31.
After mixing to dissolve the aggregating treatment agent, the solution is continuously fed to the inner tank 51 of the filtration device 5 via the electromagnetic valve 33.

【0018】ここで添加される凝集処理剤は、例えば硫
酸アルミニウム等の固体材料からなる無機凝集剤と、例
えばアクリル酸ナトリウム等の固体材料からなる高分子
凝集剤と、例えば炭酸ナトリウム等からなるpH調整剤
と、例えば炭酸カルシウム等からなる沈降剤とを混合し
て得た例えば粉末状、粒状、フレーク状等の固体系の凝
集処理剤である。
The aggregating agent added here is an inorganic aggregating agent made of a solid material such as aluminum sulfate, a polymer aggregating agent made of a solid material such as sodium acrylate, and a pH of eg sodium carbonate. It is a solid-state aggregating treatment agent, for example, in the form of powder, granules, flakes or the like, obtained by mixing a regulator and a precipitating agent such as calcium carbonate.

【0019】この凝集処理剤を添加すると、先ず無機凝
集剤が溶解してこれが凝集核となり、これに農薬廃液中
の農薬自体に含まれる鉱物や種籾のゴミや泥等の固形成
分が付着して凝集粒子が生成し、この凝集粒子に高分子
凝集剤が付着してこれがバインダーとなりさらに大きな
凝集体ができる。また沈降剤の存在により凝集核の生成
が促進されて大きな凝集体が効率的に生成され、生成し
た凝集体は沈降して凝集沈殿用混合槽3の底部に蓄積さ
れる。この際農薬廃液中に残存する農薬成分等の化学的
有害成分も凝集体に付着する。なお農薬にアニオン系あ
るいはノニオン系の界面活性剤が多量に含まれていると
凝集が起こりにくくなるため、前述のようにカチオン系
の界面活性剤を添加して、アニオン系あるいはノニオン
系の界面活性剤を不活性化することが必要である。
When this aggregating agent is added, the inorganic aggregating agent is first dissolved to form aggregating nuclei, on which solid components such as minerals and seed paddy dust and mud contained in the agrochemical itself in the agrochemical waste liquid adhere. Aggregated particles are generated, and the polymer aggregating agent adheres to the aggregated particles, and this serves as a binder to form a larger aggregate. In addition, the presence of the settling agent promotes the production of agglomerate nuclei to efficiently produce large agglomerates, and the agglomerates thus produced settle and accumulate at the bottom of the aggregating and sedimenting mixing tank 3. At this time, chemically harmful components such as pesticide components remaining in the pesticide waste liquid also adhere to the aggregates. If the pesticide contains a large amount of anionic or nonionic surfactant, aggregation will be less likely to occur.Therefore, add a cationic surfactant as described above to add anionic or nonionic surfactant. It is necessary to inactivate the agent.

【0020】ろ過装置5では内槽51を回転させること
によりろ過を行い、内槽51より外槽52へ排出された
液体分即ちろ過液は供給管53を介して中間槽6へ送ら
れる。中間槽6ではろ過液が所定量貯留されると、電磁
弁62、64を開き、ポンプ63を作動させて供給管6
1を介してろ過液槽7へろ過液が供給され、そこで貯留
される。
In the filtering device 5, the inner tank 51 is rotated to perform filtration, and the liquid component discharged from the inner tank 51 to the outer tank 52, that is, the filtrate is sent to the intermediate tank 6 via the supply pipe 53. When a predetermined amount of filtrate is stored in the intermediate tank 6, the solenoid valves 62 and 64 are opened and the pump 63 is operated to operate the supply pipe 6
The filtrate is supplied to the filtrate tank 7 via 1 and stored therein.

【0021】ろ過液槽7に貯留されたろ過液は、電磁弁
72、73を開き、ポンプ63を作動させて調節バルブ
75で流量を調節しながら、供給管71、ろ過液供給手
段81を介して吸着槽8へ供給される。吸着槽8では活
性炭中をろ過液が通過する際、ろ過液中に含まれる農薬
成分が活性炭に吸着されて除去され、農薬成分が残存し
ないろ過液が供給管84を介して外部へ放流される。
The filtrate stored in the filtrate tank 7 is opened through electromagnetic valves 72 and 73, the pump 63 is operated, and the flow rate is adjusted by the adjusting valve 75, while the supply pipe 71 and the filtrate supplying means 81 are used. Are supplied to the adsorption tank 8. When the filtrate passes through the activated carbon in the adsorption tank 8, the agricultural chemical components contained in the filtered liquid are adsorbed by the activated carbon and removed, and the filtered liquid in which the agricultural chemical component does not remain is discharged to the outside through the supply pipe 84. .

【0022】一方凝集沈殿用混合槽3の底部に蓄積した
凝集沈殿物は、バルブ35を介してろ過装置5の内槽5
1へ排出され、ろ過が行われる。そして液体分は中間槽
6へ流出され、内槽51に残った固体分即ち凝集沈殿物
は乾燥後、焼却するかまたは土壌に埋めて廃棄する。
On the other hand, the coagulated sediment accumulated at the bottom of the coagulation sedimentation mixing tank 3 is passed through the valve 35 to the inner tank 5 of the filtration device 5.
It is discharged to 1 and filtered. Then, the liquid content is flown out to the intermediate tank 6, and the solid content remaining in the inner tank 51, that is, the coagulated sediment is dried and then incinerated or buried in the soil and discarded.

【0023】なお以上の方法において、農薬にアニオン
系あるいはノニオン系の界面活性剤が含まれていないか
または使用量が少ない場合にはカチオン系界面活性剤の
添加は不要であり、調整剤槽2やそれに付属する装置も
必要ない。また凝集沈殿用混合槽3にて凝集処理した廃
液は電磁弁33を介して間欠的にろ過装置5に送液して
もよく、この場合には廃液に凝集処理剤を添加して廃液
中に含まれる農薬成分及び固形成分を凝集沈殿させた
後、上澄液を電磁弁33を介してろ過装置5へ送液す
る。
In the above method, if the pesticide does not contain an anionic or nonionic surfactant or if the amount used is small, it is not necessary to add a cationic surfactant, and the modifier tank 2 is used. Nor does it need any equipment attached to it. Further, the waste liquid which has been subjected to the coagulation treatment in the coagulation-sedimentation mixing tank 3 may be intermittently sent to the filtration device 5 via the electromagnetic valve 33. In this case, the coagulation treatment agent is added to the waste liquid and the waste liquid is added to the waste liquid. After the pesticide component and the solid component contained are coagulated and precipitated, the supernatant liquid is sent to the filtration device 5 via the solenoid valve 33.

【0024】次に本発明実施例の方法の効果を確認する
ために行った実験とその結果について説明する。農薬成
分ベノミルを950ppm、チウラムを750ppm含
有する農薬廃液2000mlに、粉末状の硫酸アルミニ
ウムからなる無機凝集剤50重量%、粉末状のアクリル
酸ナトリウムからなる高分子凝集剤5重量%、粉末状の
炭酸水素ナトリウムからなるpH調整剤25重量%、粉
末状の炭酸カルシウムなる沈降剤20重量%を混合して
調整した凝集処理剤を添加して200rpmで1分間攪
拌し、1分間静置した。その後80メッシュろ布を用い
てろ過を行ないろ液を1900ml採取し、このろ液を
活性炭を充填した吸着塔を通過させ、通過液中の農薬成
分の濃度を測定した。通過液中にはベノミル、チウラム
は検出されなかった。 この結果により、粉末状の無機
凝集剤、高分子凝集剤、pH調整剤、沈降剤を混合して
得た固体系の凝集処理剤を添加しても、液体の無機凝集
剤と高分子凝集剤を同時に添加した場合のように、無機
凝集剤と高分子凝集剤とが互いに反応して凝集作用を起
こりにくくすることはなく、高い凝集効率を得ることが
できることが確認された。これは粉末状の無機凝集剤と
高分子凝集剤を同時に添加しても、溶解速度が異なるた
め無機凝集剤が先に溶解し、凝集核となった後に、高分
子凝集剤が溶解するため、両者が互いに反応することが
ないからである。
Next, an experiment conducted to confirm the effect of the method of the embodiment of the present invention and its result will be described. In 2000 ml of pesticide waste liquid containing 950 ppm of pesticide component benomyl and 750 ppm of thiuram, 50% by weight of inorganic flocculant made of powdered aluminum sulfate, 5% by weight of polymer flocculant made of powdered sodium acrylate, powdered carbonic acid A coagulation treating agent prepared by mixing 25% by weight of a pH adjusting agent composed of sodium hydrogen and 20% by weight of a precipitation agent composed of powdery calcium carbonate was added, and the mixture was stirred at 200 rpm for 1 minute and left to stand for 1 minute. Thereafter, filtration was carried out using an 80-mesh filter cloth, 1900 ml of the filtrate was collected, this filtrate was passed through an adsorption tower filled with activated carbon, and the concentration of the pesticide component in the passed liquid was measured. Benomyl and thiuram were not detected in the permeate. From this result, even if a solid-state flocculating agent obtained by mixing a powdery inorganic flocculant, a polymer flocculant, a pH adjusting agent, and a precipitant is added, a liquid inorganic flocculant and a polymer flocculant are added. It was confirmed that high coagulation efficiency can be obtained without causing the inorganic coagulant and the polymer coagulant to react with each other to make the coagulation action less likely to occur unlike in the case of simultaneously adding. This is because even if the powdery inorganic coagulant and the polymer coagulant are added at the same time, the inorganic coagulant is dissolved first because the dissolution rate is different, and the polymer coagulant is dissolved after the coagulation nuclei are formed. This is because both do not react with each other.

【0025】また、一旦農薬廃液に凝集処理剤を添加し
て凝集沈殿物を除去した後に、活性炭による吸着処理を
行なうので、農薬成分の吸着に必要な活性炭の量を減少
できることが確認された。これは農薬廃液に凝集処理剤
を添加すると、農薬廃液中に含有する鉱物や種籾のゴ
ミ、泥等が凝集沈殿物となるが、この凝集沈殿物に農薬
成分の一部が付着し、凝集沈殿物と共に除去されるため
と考えられる。このようにこの実験結果から本発明実施
例の方法は農薬廃液の廃棄処理に適していることが確認
された。
Further, it was confirmed that the amount of activated carbon required for adsorbing pesticide components can be reduced because the coagulation treatment agent is once added to the agricultural chemical waste liquid to remove the coagulated precipitate and then the adsorption treatment with activated carbon is performed. This is because when an aggregating treatment agent is added to pesticide waste liquid, minerals, seed paddy dust, mud, etc. contained in the pesticide waste liquid become agglomerated precipitates. It is thought that this is because it is removed together with the object. As described above, it was confirmed from the results of this experiment that the method of the example of the present invention is suitable for the disposal of the agricultural chemical waste liquid.

【0026】以上に説明したように本発明実施例の廃液
処理方法では、無機凝集剤、高分子凝集剤、pH調整
剤、沈降剤を混合して得られる固体系凝集剤を使用して
いるので、凝集処理剤を1つの槽から同時に供給するこ
とができ、液体の凝集処理剤で必要であった各材料溶液
を貯留するタンクやバルブ、供給タイミングの制御が不
要であるため、装置構成や制御を簡易化することができ
る。
As described above, in the waste liquid treatment method of the embodiment of the present invention, the solid-type flocculant obtained by mixing the inorganic flocculant, the polymer flocculant, the pH adjuster and the precipitant is used. Since the aggregating agent can be simultaneously supplied from one tank and the tanks and valves for storing the material solutions required for the liquid aggregating agent and the control of the supply timing are unnecessary, the device configuration and control Can be simplified.

【0027】また固体系凝集処理剤には沈降剤が含まれ
ているため、凝集核の生成が促進されて大きな凝集体が
効率よく生成されるので、凝集処理効率を高めることが
できる。
Further, since the solid aggregating treatment agent contains a sedimentation agent, the formation of aggregating nuclei is promoted and large agglomerates are efficiently produced, so that the aggregating treatment efficiency can be enhanced.

【0028】さらに本発明実施例では農薬廃液に凝集処
理剤を添加して、凝集沈殿物を除去した後に、ろ過液に
活性炭を添加して残存する農薬成分を吸着させて除去し
ているので、農薬成分の除去に必要な活性炭の量を従来
の約1/10に低減でき、ランニングコストを低くする
ことができる。
Further, in the present invention, since the coagulation treatment agent is added to the agricultural chemical waste liquid to remove the coagulated precipitate, activated carbon is added to the filtrate to adsorb and remove the residual agricultural chemical components. The amount of activated carbon required to remove pesticide components can be reduced to about 1/10 of the conventional amount, and the running cost can be reduced.

【0029】[0029]

【発明の効果】本発明の廃液処理方法によれば、固体系
の凝集処理剤を用いると共に、廃液に凝集処理剤を添加
して廃液に含有する化学的有害成分と固形成分とを凝集
させて除去した後に、活性炭に残存する化学的有害成分
を吸着させて除去しているので、装置の構成及び制御を
簡易化することができ、また処理効率を向上させること
ができる。
According to the waste liquid treatment method of the present invention, a solid-type aggregating treatment agent is used, and the aggregating treatment agent is added to the waste liquid to aggregate the chemically harmful components and the solid components contained in the waste liquid. After the removal, the chemically harmful components remaining on the activated carbon are adsorbed and removed, so that the configuration and control of the device can be simplified and the processing efficiency can be improved.

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

【図1】本発明方法を実施するための廃液処理装置の一
例を示す構成図である。
FIG. 1 is a configuration diagram showing an example of a waste liquid treatment apparatus for carrying out the method of the present invention.

【符号の説明】[Explanation of symbols]

1 廃液貯留槽 3 凝集沈殿用混合槽 4 フィーダー 5 ろ過装置 7 ろ過液槽 8 吸着槽 82 活性炭 1 Waste liquid storage tank 3 Coagulation sedimentation mixing tank 4 Feeder 5 Filtration device 7 Filtration liquid tank 8 Adsorption tank 82 Activated carbon

───────────────────────────────────────────────────── 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 1/28 ZAB D 1/56 ZAB Z 9042−4D ─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Internal reference number FI Technical display location C02F 1/28 ZAB D 1/56 ZAB Z 9042-4D

Claims (1)

【特許請求の範囲】[Claims] 【請求項1】 廃液に固体材料からなる無機凝集剤と、
高分子凝集剤と、pH調整剤と、沈降剤とを含む固体系
凝集処理剤を添加し、廃液に含有する化学的有害成分と
固形成分とを凝集させる工程と、 前記凝集処理剤が添加された廃液をろ過する工程と、 この工程により得られたろ過液を活性炭に接触させて当
該液中に含まれる化学的有害成分を吸着させて除去する
工程と、 この工程で得られた処理液を排出する工程と、 からなることを特徴とする廃液処理方法。
1. An inorganic coagulant made of a solid material in the waste liquid,
A step of adding a solid-state aggregating agent containing a polymer aggregating agent, a pH adjuster, and a settling agent, and aggregating a chemically harmful component and a solid component contained in the waste liquid, and the aggregating agent is added. The step of filtering the waste liquid, the step of contacting the filtered liquid obtained in this step with activated carbon to adsorb and remove the chemical harmful components contained in the liquid, and the treatment liquid obtained in this step A waste liquid treatment method comprising the step of discharging.
JP5252281A 1993-09-14 1993-09-14 Treatment of waste liquid Pending JPH0780497A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP5252281A JPH0780497A (en) 1993-09-14 1993-09-14 Treatment of waste liquid

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP5252281A JPH0780497A (en) 1993-09-14 1993-09-14 Treatment of waste liquid

Publications (1)

Publication Number Publication Date
JPH0780497A true JPH0780497A (en) 1995-03-28

Family

ID=17235070

Family Applications (1)

Application Number Title Priority Date Filing Date
JP5252281A Pending JPH0780497A (en) 1993-09-14 1993-09-14 Treatment of waste liquid

Country Status (1)

Country Link
JP (1) JPH0780497A (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US7491337B2 (en) 2004-04-23 2009-02-17 Jeffbrad Investments Pty Limited Method and apparatus for removing contaminants from water
WO2009087259A1 (en) * 2008-01-11 2009-07-16 Universidad De Jaén Method for the treatment of water originating from the washing of agricultural products
KR101371360B1 (en) * 2012-06-14 2014-03-07 한국과학기술연구원 Apparatus and method for phosphorous removal from waste water using dolomite

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US7491337B2 (en) 2004-04-23 2009-02-17 Jeffbrad Investments Pty Limited Method and apparatus for removing contaminants from water
WO2009087259A1 (en) * 2008-01-11 2009-07-16 Universidad De Jaén Method for the treatment of water originating from the washing of agricultural products
ES2324141A1 (en) * 2008-01-11 2009-07-30 Universidad De Jaen PROCEDURE FOR WATER TREATMENT FROM WASHING OF AGRICULTURAL PRODUCTS.
KR101371360B1 (en) * 2012-06-14 2014-03-07 한국과학기술연구원 Apparatus and method for phosphorous removal from waste water using dolomite

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