JP2532293B2 - Flocculant and manufacturing method thereof - Google Patents

Flocculant and manufacturing method thereof

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Publication number
JP2532293B2
JP2532293B2 JP2106554A JP10655490A JP2532293B2 JP 2532293 B2 JP2532293 B2 JP 2532293B2 JP 2106554 A JP2106554 A JP 2106554A JP 10655490 A JP10655490 A JP 10655490A JP 2532293 B2 JP2532293 B2 JP 2532293B2
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JP
Japan
Prior art keywords
flocculant
water
incineration ash
sulfuric acid
ash
Prior art date
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Expired - Lifetime
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JP2106554A
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Japanese (ja)
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JPH047004A (en
Inventor
佐内 藤田
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Individual
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Individual
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Priority to JP2106554A priority Critical patent/JP2532293B2/en
Priority to KR1019900008074A priority patent/KR910018057A/en
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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D21/00Separation of suspended solid particles from liquids by sedimentation
    • B01D21/01Separation of suspended solid particles from liquids by sedimentation using flocculating agents

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  • Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Separation Of Suspended Particles By Flocculating Agents (AREA)

Description

【発明の詳細な説明】 (産業上の利用分野) 本発明は、生ゴミ焼却灰を利用した動物骨含有凝集
剤、及びその製法に関する。
TECHNICAL FIELD The present invention relates to an animal bone-containing flocculant using food waste incineration ash, and a method for producing the same.

(従来の技術) 人類が開発した近代産業、工業によって新しい文化が
生み出されているが、その反面、それに伴って自然環境
に大きな影響を与え、自然の浄化作用を越えて自然の破
壊や汚染が発生している。
(Prior art) Although new culture is created by modern industries and industries developed by humankind, on the other hand, it also has a great impact on the natural environment and destroys and pollutes nature beyond the purifying action of nature. It has occurred.

人類が常に健康で文化的な生活を確保するためには、
産業の発達と共にその悪影響を取り除いて生活の発展に
適した新しい環境を作り出していく必要がある。その一
番身近な生活公害の生ゴミ焼却灰処理問題が日本のみな
らず世界各国の悩みとなっている。
In order for humanity to always have a healthy and cultural life,
It is necessary to eliminate the adverse effects of industrial development and create a new environment suitable for the development of life. The problem of incineration of garbage, which is the closest to life, has become a problem not only in Japan but also around the world.

この生ゴミ焼却灰処理問題については各国の各関係機
関等で色々と研究されているが、抜本的な解決策は見出
されていないのが現状である。
Although various institutes in each country have been researching various problems related to the incineration ash treatment of raw garbage, the present situation is that no drastic solution has been found.

一方、廃水中の有機物を凝集させる凝集剤としては従
来、硫酸バンド、塩化アルミニウム、第二塩化鉄等が知
られている。また、有機物を含む廃水は通常、活性汚泥
法により処理されてきた。しかしながら、従来の凝集剤
はいずれも酸性側で反応するものであって処理水が酸性
とならざるを得ず、放流による環境汚染の問題が残され
ていた。しかも、上記凝集剤では一般の公共水道水や汚
染度の低い水では反応せず、かなり汚れた廃水に対して
機能するものであった。また、従来の活性汚泥法では、
動物性の腐敗性有機物を含む廃水をこの活性汚泥法で処
理した場合、これによって得られる処理水の水質は放流
することができる基準値を満たすものであるが、PHは酸
性、BOD,CODはともに30〜60ppm程度、臭気が完全には除
去されない等、自然水域に無害であるという意味におい
ては、必ずしも十分な水質とは言えないものであった。
また、上記処理水では、工場用水や洗浄用水等として再
利用するには不適であった。さらに、活性汚泥槽を微生
物が繁殖活動できる20〜30℃に保つと同時に、酸素供給
のための曝気が常時必要であり、有機物が適量に存在し
なければならない等の条件整備が必要であると共に、処
理時間はかなり長時間を要していた。また、複雑かつ大
規模な設備が必要であり、設備費は多大であり、メンテ
ナンス費用及び労力も過大であった。
On the other hand, sulfuric acid bands, aluminum chloride, ferric chloride, etc. are conventionally known as coagulants for coagulating organic substances in wastewater. In addition, wastewater containing organic substances has usually been treated by the activated sludge method. However, all of the conventional flocculants react on the acidic side, and the treated water is inevitably acidic, and the problem of environmental pollution due to discharge remains. Moreover, the above coagulant did not react with general public tap water or water with a low degree of pollution, and it worked against considerably contaminated waste water. In addition, in the conventional activated sludge method,
When wastewater containing animal spoilage organic matter is treated by this activated sludge method, the quality of the treated water obtained by this treatment satisfies the standard value that can be discharged, but PH is acidic, BOD, COD is The water quality was not sufficient in the sense that it was harmless to natural waters, such as odor was not completely removed at about 30 to 60 ppm.
Further, the treated water was not suitable for reuse as factory water, cleaning water, or the like. Furthermore, it is necessary to keep the activated sludge tank at 20 to 30 ° C where microorganisms can reproduce, and at the same time to constantly aerate for oxygen supply, and it is necessary to prepare conditions such that organic matter must exist in an appropriate amount. The processing time was quite long. Further, complicated and large-scale equipment is required, the equipment cost is large, and the maintenance cost and labor are excessive.

(発明が解決しよとする課題) 本発明は、中性ないしアルカリ性で反応して処理水の
放流による環境汚染の虞れを防止し、一般の公共水道水
ないし同程度の水でも反応する高反応性を有すると共
に、従来のものに比して極めて少ない使用量で十分な機
能を発揮し、しかもフロックの形成が早く分離速度の大
きい凝集剤を提供せんとするものである。また本発明は
生ゴミ焼却灰を利用することにより生ゴミ焼却灰処理問
題を解決する一つの有力な方法を提供するものである。
(Problems to be Solved by the Invention) The present invention prevents the risk of environmental pollution due to discharge of treated water by reacting with neutrality or alkalinity, and can react with general public tap water or similar water. The present invention provides a flocculant which has reactivity, exhibits a sufficient function with an extremely small amount of use as compared with the conventional one, and has a fast floc formation and a high separation rate. Further, the present invention provides one powerful method for solving the problem of treating garbage incineration ash by utilizing the garbage incineration ash.

(課題を解決するための手段) 本発明は、生ゴミ焼却灰、動物骨粉及び亜鉛を硫酸ま
たは塩酸、及び水と混合し溶解してなる凝集剤及びその
製法である。
(Means for Solving the Problem) The present invention is a flocculant obtained by mixing and dissolving raw garbage incinerated ash, animal bone powder and zinc with sulfuric acid or hydrochloric acid, and water, and a method for producing the same.

生ゴミは日常生活により排出されるゴミであり、生ゴ
ミ焼却灰には通常、有機物、強熱減量成分、フミン酸、
残さ(二酸化ケイ素)、金属類及び有害金属、等が含ま
れる。
Raw garbage is the garbage discharged in daily life, and the organic matter, ignition loss component, humic acid,
Residues (silicon dioxide), metals and harmful metals, etc. are included.

本発明の生ゴミ焼却灰としては有害重金属を実質的に
含まない生ゴミ焼却灰が好ましい。この有害重金属を含
まない生ゴミ焼却灰粉はアルカリ性であり、生ゴミ焼却
灰粉から有害重金属(水銀、カドミウム、鉛)を除いた
もの、または生ゴミを焼却する際に重金属を除去しつつ
焼成して得られた焼成灰粉、例えば重金属を吸着する吸
着材の存在下に水銀、カドミウム、鉛、クロム等を吸着
させつつ焼却して得られた焼却灰粉であり、必要に応じ
クロム等を添加したものである。
As the organic waste incineration ash of the present invention, organic waste incineration ash substantially free of harmful heavy metals is preferable. This incinerator ash powder that does not contain harmful heavy metals is alkaline, and the ash powder that incinerates garbage does not contain harmful heavy metals (mercury, cadmium, lead), or is burned while removing the heavy metals when incinerating the garbage. Fired ash powder obtained by, for example, incineration ash powder obtained by incineration while adsorbing mercury, cadmium, lead, chromium, etc. in the presence of an adsorbent that adsorbs heavy metals, and if necessary, chromium etc. It was added.

本発明で有害重金属を実質的に含まない生ゴミ焼却灰
は、通常、生ゴミ焼却灰1kg当たり、アルキル水銀0.05m
g以下、カドミウム1mg以下、鉛10mg以下、六価クロム5m
g以下であり、好ましくはこれら重金属が検出されない
焼却灰粉である。
The garbage incineration ash that does not substantially contain harmful heavy metals in the present invention is usually 0.05 m of alkyl mercury per 1 kg of garbage incineration ash.
g or less, cadmium 1 mg or less, lead 10 mg or less, hexavalent chromium 5 m
It is g or less, preferably incinerated ash powder in which these heavy metals are not detected.

本発明においてはこの焼却灰は、通常、硫酸または塩
酸に溶解した形態で凝集剤の原料として用い、動物骨
粉、亜鉛、水と混合して凝集剤を調製する。
In the present invention, this incinerated ash is usually used as a raw material of the flocculant in a form dissolved in sulfuric acid or hydrochloric acid, and mixed with animal bone powder, zinc and water to prepare the flocculant.

その割合は通常、動物骨粉100重量部に対して、焼却
灰は100〜550重量部、好ましくは150〜400重量部であ
り、焼却粉の量が100重量部より少ないと凝集速度を増
大させる焼却灰の効果が少なくなり、550重量部を越え
ると動物骨粉による凝集効果が低下する。
The proportion is usually 100 to 550 parts by weight of animal bone powder, incineration ash is 100 to 550 parts by weight, preferably 150 to 400 parts by weight, incineration to increase the aggregation rate when the amount of incinerated powder is less than 100 parts by weight. The effect of ash decreases, and when it exceeds 550 parts by weight, the aggregating effect of animal bone powder decreases.

凝集剤中における動物骨粉と焼却灰の合計量は液中に
硫酸または塩酸の量によって変わるがいずれにしても室
温においてこれらが液中に溶解し得る量以下である。
The total amount of animal bone powder and incinerated ash in the flocculant varies depending on the amount of sulfuric acid or hydrochloric acid in the liquid, but in any case, these are not more than the amount that can dissolve in the liquid at room temperature.

また動物骨粉は、従来畜産場等で殆ど廃棄されていた
骨、特に牛、馬、羊等の硬骨が主体の動物の骨が採用さ
れる。
As animal bone powder, bones that have been mostly discarded in the past at livestock farms, especially bones of animals mainly composed of hard bones such as cows, horses, and sheep, are adopted.

これらの動物の生骨は焼却しやすい大きさに切断し、
その上で圧力釜に投入し、200〜400℃前後で、約90分前
後煮沸する。次いでこの骨を焼成炉に入れ、900〜1100
℃前後で、60〜180分前後焼成し、そのまま炉内で60分
前後自然冷却させて室温乃至しこれに近い状態に戻す。
Raw bones of these animals are cut into a size that is easy to incinerate,
Then put into a pressure cooker and boil at about 200-400 ° C for about 90 minutes. Then put this bone in a firing furnace, 900-1100
Bake for about 60 to 180 minutes at about ℃, and let it cool in the furnace for about 60 minutes to return to room temperature or a state close to this.

骨に骨成分以外のゼラチン、脂肪、蛋白質、にかわ等
の有機物が残存すると酸化腐敗の原因となるので、これ
を確実に除去しておくことが重要である。上記煮沸工程
によって、外側のみならず気孔内に付着している有機物
を骨から大方分離除去することができる。
It is important to remove the organic substances such as gelatin, fats, proteins, and glues other than the bone components remaining in the bones because they may cause oxidative rot. By the boiling step, organic substances adhering not only to the outside but also to the pores can be largely separated and removed from the bone.

その上で上記焼成工程を通すことによって、残存する
有機物を完全に除去することができ、同時に骨中の湿度
(水分)を数%以下、好ましくはほぼ0%にまで低下さ
せることができる。上記焼成条件によれば、骨に白骨化
して無数の気孔を有した原形組織状態を維持する。
By passing through the above-mentioned baking step, the remaining organic substances can be completely removed, and at the same time, the humidity (moisture) in the bone can be reduced to several% or less, preferably to almost 0%. According to the above-mentioned firing conditions, the original tissue state in which the bone is whitened and has numerous pores is maintained.

上記焼成、冷却後、この骨を破砕し、パウダー機にか
けて20〜200メッシュ前後、特に好ましくは50〜100メッ
シュの粉状の骨粉とする。
After firing and cooling as described above, the bone is crushed and powdered into a powdery bone meal of about 20 to 200 mesh, particularly preferably 50 to 100 mesh.

上記骨粉は、牛骨の場合、原料の生骨に比して重量比
約40%の収量で得られる。粒子は、カルシウム(約33重
量%)を主成分とし、リン(約16.7%)、バリウム(約
1.03%)、ナトリウム(約0.76%)、イオウ(約0.64
%)、他にマグネシウム、カリウム、塩素、アミン、鉄
等からなっており、粒子の内外に渡って無数の微小気孔
が連通存在している。この骨粉はカルシウムを含有する
ためにアルカリ性である。
In the case of bovine bone, the bone meal can be obtained in a yield of about 40% by weight as compared with raw bone as a raw material. Particles are mainly composed of calcium (about 33% by weight), phosphorus (about 16.7%), barium (about
1.03%), sodium (about 0.76%), sulfur (about 0.64)
%) In addition to magnesium, potassium, chlorine, amine, iron, etc., and countless micropores are continuously present inside and outside the particles. This bone meal is alkaline because it contains calcium.

動物骨粉そのまま、または硫酸もしくは塩酸の溶液と
して、他の原料と混合して凝集剤の調製に用いる。
Animal bone meal as it is or as a solution of sulfuric acid or hydrochloric acid is mixed with other raw materials and used for the preparation of the flocculant.

本発明においては凝集剤の成分の一つとして亜鉛を含
有するが、この亜鉛もそのまま、または硫酸もしくは塩
酸の溶液として用いるが、通常、後者の溶液の状態で使
用する。水は焼却灰等の粉体を溶解したり、濃度を調節
するために用いる。
In the present invention, zinc is contained as one of the components of the flocculant, and this zinc is also used as it is or as a solution of sulfuric acid or hydrochloric acid, but it is usually used in the state of the latter solution. Water is used to dissolve powder such as incinerated ash and to adjust the concentration.

本発明の凝集剤は中性ないしアルカリ性で効果的に反
応する。そのためにPHが酸性領域の廃水等に対しては、
これを中性ないしアルカリ性にするために、上記凝集剤
と同時に水酸化ナトリウム、水酸化カルシウム等のアル
カリ性反応剤を廃水に混合して使用するのがよい。また
PHが9.5以上の場合は希硫酸等の酸性反応剤を用いるの
が好ましい。
The flocculant of the present invention is neutral or alkaline and reacts effectively. Therefore, for wastewater in which PH is acidic,
In order to make it neutral or alkaline, it is preferable to use an alkaline reaction agent such as sodium hydroxide or calcium hydroxide mixed with the waste water together with the coagulant. Also
When the pH is 9.5 or more, it is preferable to use an acidic reactant such as dilute sulfuric acid.

本発明の凝集剤は前記の原料成分を混合し溶解するこ
とによって得られるが、通常、有害重金属を実質的に含
まない生ゴミ焼却灰を硫酸または塩酸に溶解した焼却灰
溶液を得て、この溶液と動物骨粉、亜鉛及び水を混合し
均一化することによって製造する。混合後は、加熱、撹
拌し、次いで濾過して不溶解分を分離し、溶液を凝集剤
として回収するのが好ましい。
The flocculant of the present invention is obtained by mixing and dissolving the above-mentioned raw material components, but normally, an incinerator ash solution obtained by dissolving raw garbage incineration ash substantially containing no harmful heavy metal in sulfuric acid or hydrochloric acid is used. It is prepared by mixing the solution with animal bone meal, zinc and water and homogenizing. After mixing, it is preferable to heat and stir, and then filter to separate the insoluble matter and recover the solution as a flocculant.

凝集剤の製造の一態様を示すと次のとおりである。有
害重金属を実質的に含まない生ゴミ焼却灰700gを濃硫酸
に溶解し、牛骨粉300g、亜鉛20g(硫酸に溶解したも
の)に水50lを加える。水を加えると発熱する。180℃で
30〜60分、撹拌しながら全体が約1Kgになるまで煮詰め
た後、濾過し、凝集剤を得る。
One mode of producing the aggregating agent is as follows. 700 g of garbage incineration ash that does not substantially contain harmful heavy metals is dissolved in concentrated sulfuric acid, and 300 g of beef bone powder and 20 g of zinc (dissolved in sulfuric acid) are added with 50 l of water. Heat is generated when water is added. At 180 ° C
The mixture is boiled for 30 to 60 minutes with stirring until the total amount becomes about 1 kg, and then filtered to obtain a flocculant.

(発明の効果) 本発明の凝集剤は生ゴミ焼却灰を利用するものであ
り、生ゴミ焼却灰処理問題を解決する一つの有力な手段
となり得る。
(Effects of the Invention) The flocculant of the present invention uses the incineration ash of garbage, and can be one of the powerful means for solving the problem of incinerating ash of garbage.

本発明の凝集剤は画期的なものであり、中性ないしア
ルカリ性で反応するため処理水の放流による環境汚染の
おそれが防止でき、高反応性を有するので一般の公共水
道水ないし同程度の水にも適用でき、従来のものに比し
て極めて少ない使用量で十分な機能を発揮し、しかもフ
ロックの形成が早く分離速度が大きい、という顕著な効
果を達成し得る。
The flocculant of the present invention is epoch-making, and since it reacts with neutrality or alkalinity, it is possible to prevent the risk of environmental pollution due to the discharge of treated water. It can be applied to water and can exert a sufficient function with an extremely small amount of use as compared with the conventional one, and can achieve a remarkable effect that the formation of flocs is fast and the separation speed is high.

(実施例) 凝集剤の製造 生ゴミ焼却灰700gを濃硫酸に溶解し、牛骨粉300g、亜
鉛20g(硫酸に溶解したもの)に水50lを加えた。水を加
えると発熱した。180℃で約45分、撹拌しながら全体が
約1kgになるまで煮詰めた後、濾過し、凝集剤を得た。
(Example) Production of flocculant 700 g of garbage incineration ash was dissolved in concentrated sulfuric acid, and 300 g of beef bone powder and 20 g of zinc (dissolved in sulfuric acid) were added with 50 l of water. The addition of water caused an exotherm. The mixture was boiled at 180 ° C. for about 45 minutes with stirring until the total amount became about 1 kg, and then filtered to obtain a flocculant.

凝集剤の試験 ガソリンスタンドの排水(洗車後の排水が主体のも
の)を取水し、試験管に8分目位入れ、アルカリ粉末を
加えてPHをほぼ中性にした後、上記凝集剤を1〜2滴加
え、振り混ぜたところ、凝集剤添加の10秒後にはフロッ
クが生成し、それとほぼ同時に試験管の上部に油とフロ
ック、下部に水層が分離した。
Flocculant test Drainage from gas stations (mainly drained after car wash) was taken, placed in a test tube for 8 minutes, and alkali powder was added to neutralize PH. When ~ 2 drops were added and shaken, flocs were formed 10 seconds after the addition of the coagulant, and at the same time, oil and flocs were separated on the upper part of the test tube and an aqueous layer was separated on the lower part.

比較のため、上記の凝集剤の代わりに硫酸バンドを加
えて振り混ぜたところ、フロックの形成に30秒に要し、
次いで分離に30分を要し、上部に油、中間分に水層、下
部にフロックが分離した。
For comparison, when a sulfuric acid band was added instead of the above flocculant and shaken, it took 30 seconds to form flocs,
Then, it took 30 minutes for separation, and oil was separated in the upper part, an aqueous layer was separated in the middle part, and flocs were separated in the lower part.

Claims (4)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】生ゴミ焼却灰、動物骨粉及び亜鉛を硫酸又
は塩酸、及び水と混合し溶解してなる凝集剤。
1. A flocculant obtained by mixing raw incineration ash, animal bone powder and zinc with sulfuric acid or hydrochloric acid and water and dissolving them.
【請求項2】請求項(1)記載の凝集剤を該凝集剤によ
り処理される処理水に使用する際に、アルカリ性反応剤
を該処理水に添加した上で使用することを特徴とする請
求項(1)記載の凝集剤の使用方法。
2. When the coagulant according to claim 1 is used in treated water treated with the coagulant, an alkaline reactive agent is added to the treated water before use. A method of using the aggregating agent according to item (1).
【請求項3】生ゴミ焼却灰を硫酸又は塩酸に溶解した焼
却灰溶液を得、この溶液と動物骨粉、亜鉛及び水を混合
し均一化することを特徴とする凝集剤の製法。
3. A method for producing a flocculant, which comprises obtaining an incineration ash solution in which raw garbage incineration ash is dissolved in sulfuric acid or hydrochloric acid, and mixing this solution with animal bone meal, zinc and water to homogenize them.
【請求項4】混合後、加熱、攪拌し、次いで濾過して濾
液を凝集剤として回収する請求項(3)記載の凝集剤の
製法。
4. The method for producing a flocculant according to claim 3, wherein the mixture is heated, stirred, and then filtered to recover the filtrate as a flocculant.
JP2106554A 1990-04-24 1990-04-24 Flocculant and manufacturing method thereof Expired - Lifetime JP2532293B2 (en)

Priority Applications (2)

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JP2106554A JP2532293B2 (en) 1990-04-24 1990-04-24 Flocculant and manufacturing method thereof
KR1019900008074A KR910018057A (en) 1990-04-24 1990-05-31 Flocculant, preparation method thereof and method of use

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2106554A JP2532293B2 (en) 1990-04-24 1990-04-24 Flocculant and manufacturing method thereof

Publications (2)

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JPH047004A JPH047004A (en) 1992-01-10
JP2532293B2 true JP2532293B2 (en) 1996-09-11

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2004080499A1 (en) * 2003-03-12 2004-09-23 3M Innovative Properties Company Polymer compositions with bioactive silver, copper or zinc compounds, medical articles, and processes
JP4216894B2 (en) 2005-12-26 2009-01-28 株式会社エクセラ Flocculant
FR2950619B1 (en) * 2009-09-25 2011-12-09 Serge Ferlay PROCESS FOR DEULFATATION OF ACID RELEASES FROM THE TITANIUM INDUSTRY
JP5770538B2 (en) * 2011-06-07 2015-08-26 堀邊 義一 Treatment method of palm waste oil

Also Published As

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KR910018057A (en) 1991-11-30
JPH047004A (en) 1992-01-10

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