JPH01274807A - Coagulant containing animal bone, and its production and using the coagulant - Google Patents

Coagulant containing animal bone, and its production and using the coagulant

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Publication number
JPH01274807A
JPH01274807A JP10558088A JP10558088A JPH01274807A JP H01274807 A JPH01274807 A JP H01274807A JP 10558088 A JP10558088 A JP 10558088A JP 10558088 A JP10558088 A JP 10558088A JP H01274807 A JPH01274807 A JP H01274807A
Authority
JP
Japan
Prior art keywords
animal bone
tank
bone
coagulant
solution
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
JP10558088A
Other languages
Japanese (ja)
Other versions
JPH0553521B2 (en
Inventor
Sanai Fujita
佐内 藤田
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.)
Individual
Original Assignee
Individual
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 Individual filed Critical Individual
Priority to JP10558088A priority Critical patent/JPH01274807A/en
Priority to CA 584061 priority patent/CA1335153C/en
Priority to US07/276,265 priority patent/US5047255A/en
Priority to NZ22709388A priority patent/NZ227093A/en
Priority to AU25911/88A priority patent/AU623613B2/en
Publication of JPH01274807A publication Critical patent/JPH01274807A/en
Priority to US07/756,809 priority patent/US5254285A/en
Priority to US08/088,160 priority patent/US5397499A/en
Publication of JPH0553521B2 publication Critical patent/JPH0553521B2/ja
Priority to US08/373,004 priority patent/US5487844A/en
Granted legal-status Critical Current

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  • Separation Of Suspended Particles By Flocculating Agents (AREA)

Abstract

PURPOSE:To obtain high reactivity of a coagulant contg. animal bones for a small amt. of the coagulant used thereby even in an alkaline region by prepg. the coagulant from a soln. obtd. by mixing uniformly a bone soln. of animal bone powder in H2SO4, etc., with a soln. of a metal such as iron and copper in sulfuric acid, etc. CONSTITUTION:Domestic waste water is in a first stage introduced into a measuring tank 3 where an amt. of a coagulant or a reagent is adjusted. When the waste water flows into a stirring tank 4, a coagulant is fed at the same time from a tank 1 for a coagulant contg. animal bone, and a reagent such as slaked lime is fed from a reagent tank 2, and the mixture is stirred. Then, the mixture is forced to a pressurized floating tank 5 with a compressor, and treated water passed through a skimmer at the top of the tank 5 is discharged or reutilized through a filtration tank 6. In this stage, the animal bone powder in the coagulant to the stirring tank 4 makes the atmosphere caustic with Ca ions, etc., in the composition and coagulates org. matters. Further, metals in the compsn. coagulate the org. matters more firmly, and facilitate settling of coagulated products by increasing the weight of the coagulated products.

Description

【発明の詳細な説明】 (産業上の利用分野) 本発明は、凝集剤詳しくは廃水等の処理液中の有機物凝
集に特に効果的な動物骨含有凝集剤、その製法と使用方
法に関する。
DETAILED DESCRIPTION OF THE INVENTION (Industrial Application Field) The present invention relates to a flocculant, and more particularly to an animal bone-containing flocculant that is particularly effective for flocculating organic matter in treated liquids such as wastewater, and methods for producing and using the same.

(従来の技術) 従来、廃水中の有機物等を凝集する凝集剤として、硫酸
バンド−1塩化アルミニウムポリマー、第2塩化鉄等が
存在している。
(Prior Art) Conventionally, sulfate-1 aluminum chloride polymer, ferric chloride, and the like have been used as flocculants for flocculating organic substances and the like in wastewater.

一方、有機物を含む廃水処理の従来方法は、主として活
性汚泥法で行われてきた。活性汚泥法は、バクテリア等
の微生物を増殖させ、これにより汚泥中の有機物を吸着
させ、不純物を沈降分離させるものであり、高い浄化能
力を有している。活性汚泥法によった処理水は、一定の
水質基準を満足する状態において、そのまま河川等に放
流されていた。
On the other hand, the conventional method for treating wastewater containing organic matter has mainly been an activated sludge method. The activated sludge method allows microorganisms such as bacteria to grow, thereby adsorbing organic matter in the sludge and separating impurities by sedimentation, and has a high purification ability. Water treated by the activated sludge method was discharged directly into rivers, etc., as long as it met certain water quality standards.

(発明が解決しようとする課題) しかしながら、上記従来の凝集剤はいずれも酸性側で反
応するものであるので、処理水が酸性とならざるを得す
、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。
(Problems to be Solved by the Invention) However, since all of the above conventional flocculants react on the acidic side, there remains the problem that the treated water becomes acidic and environmental pollution due to discharge. Ta. Moreover,
The above-mentioned flocculants did not react with general public tap water or water with a low degree of contamination, but functioned with considerably contaminated wastewater.

本発明は、上記に鑑み、中性乃至アルカリ域で反応する
ようにして、処理水の放流による環境汚染のおそれを防
止し、一般の公共水道水乃至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、極めて少な
い使用量で充分な機能を発揮する凝集剤を提供せんとす
るものである。
In view of the above, the present invention prevents the risk of environmental pollution due to discharge of treated water by reacting in a neutral or alkaline range, and has high reactivity that reacts with ordinary public tap water or water of the same level. It is an object of the present invention to provide a flocculant that has the same properties as conventional flocculants and exhibits sufficient functionality with an extremely small amount used compared to conventional ones.

一方、従来の活性汚泥法では、動物性等の腐敗性有機物
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、B OD −C
OD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。
On the other hand, in the conventional activated sludge method, when wastewater containing putrefactive organic matter such as animal matter is treated with this activated sludge method, the quality of the treated water obtained by this method satisfies the standard value that allows it to be discharged. However, PH is acidic, B OD -C
The OD was about 30 to 60 ppm in both cases, and the odor was not completely removed, so the water quality could not necessarily be said to be sufficient in terms of being harmless to natural water bodies.

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。又、複雑かつ
大規模な設備が必要であり、設備費は多大の費用を要し
、メンテナンス費用と労力も過大であった。
Furthermore, the above-mentioned treated water was not suitable for reuse as factory water, washing water, or the like. Furthermore, it is necessary to maintain conditions such as keeping the activated sludge tank at a temperature of 20 to 30 degrees Celsius where microorganisms can reproduce, as well as constant aeration to supply oxygen and the presence of an appropriate amount of organic matter. , the processing time was quite long. Moreover, complicated and large-scale equipment is required, and the equipment cost is large, and maintenance costs and labor are also excessive.

そこで本発明は、廃水の不純物の分離にバクテリア等の
微生物を利用するという従来の活性汚泥法とは異なって
、条件設定の簡潔な手段として用いることができ、しか
も設備やメンテナンスが簡単かつ小規模な手段により、
短時間で、廃水、特に動物性等の腐敗性有機物を含む廃
水を脱臭、殺菌、浄化し、水道水と同等以上の水質の再
生水が得られ、自然水域に放流しても汚濁の危険性がな
いのみならず、広範囲での再利用にも適した再生水が得
られる廃水処理に特に適した動物骨含有凝集剤を提供し
、効率的な廃水処理を可能にぜんとする目的をも持つも
のである。
Therefore, unlike the conventional activated sludge method that uses microorganisms such as bacteria to separate impurities in wastewater, the present invention can be used as a simple means of setting conditions, and the equipment and maintenance are simple and small-scale. By means of
In a short time, it deodorizes, sterilizes, and purifies wastewater, especially wastewater containing putrefactive organic matter such as animal matter, producing recycled water with a quality equal to or better than that of tap water, and there is no risk of pollution even when it is released into natural water bodies. The purpose of this invention is to provide an animal bone-containing flocculant that is particularly suitable for wastewater treatment, yielding reclaimed water suitable for wide-scale reuse, and to enable efficient wastewater treatment. be.

く課題を解決するための手段) 上記目的を達成するために本発明は、吸着性を有し、ア
ルカリイオン化する動物骨に着眼してなしたものであり
、その要旨は、焼成粉状化された動物骨粉を硫酸又は塩
酸に溶かしてなる骨溶解液からなる動物骨含有凝集剤、
及び、焼成粉状化された動物骨粉を硫酸又は塩酸に溶か
してなる骨溶解液と、鉄乃至銅を硫酸又は塩酸に溶かし
てなる金属溶解液とが均一に混合されてなる動物骨含有
凝集剤にある。また、焼成粉状化された動物骨粉と硫酸
又は塩酸を混合した上で骨溶解液を得、−方、鉄乃至銅
と硫酸乃至塩酸を混合した上で金属溶解液を得、その上
で両液を混合一体化することを特徴とする動物骨含有凝
集剤の製造方法にあり、かつまた、焼成粉状化された動
物骨粉を硫酸又は塩酸に溶かしてなる骨溶解液からなる
動物骨含有凝集剤を、処理液にアルカリ性反応材を添加
した上で添加使用することを特徴とする動物骨含有凝集
剤の使用方法、並びに、焼成粉状化された動物骨粉を硫
酸又は塩酸に溶かしてなる骨溶解液と、鉄乃至銅を硫酸
又は塩酸に溶かしてなる金属溶解液とが均一に混合され
てなる動物骨含有凝集剤を、処理液にアルカリ性反応材
を添加した上で添加使用することを゛特徴とする動物骨
含有U集剤の使用方法にある。
Means for Solving the Problems) To achieve the above object, the present invention has been made by focusing on animal bones that have adsorption properties and are ionized into alkali. an animal bone-containing flocculant consisting of an osteolytic solution prepared by dissolving animal bone powder in sulfuric acid or hydrochloric acid;
and an animal bone-containing flocculant, which is obtained by uniformly mixing a bone dissolving solution obtained by dissolving calcined powdered animal bone powder in sulfuric acid or hydrochloric acid, and a metal dissolving solution obtained by dissolving iron or copper in sulfuric acid or hydrochloric acid. It is in. Alternatively, a bone solution can be obtained by mixing calcined powdered animal bone powder with sulfuric acid or hydrochloric acid, and a metal solution can be obtained by mixing iron or copper with sulfuric or hydrochloric acid. A method for producing an animal bone-containing flocculant characterized by mixing and integrating liquids, and also comprising an osteolytic solution obtained by dissolving calcined and powdered animal bone powder in sulfuric acid or hydrochloric acid. A method for using an animal bone-containing flocculant, which is characterized in that the animal bone-containing flocculant is used after adding an alkaline reactive material to a treatment solution, and bone obtained by dissolving calcined and powdered animal bone powder in sulfuric acid or hydrochloric acid. An animal bone-containing flocculant, which is a uniform mixture of a solution and a metal solution prepared by dissolving iron or copper in sulfuric acid or hydrochloric acid, is used after adding an alkaline reactant to the treatment solution. The feature lies in the method of using the animal bone-containing U-collection agent.

上記製造方法においては、焼成粉状化された動物骨粉と
硫酸又は塩酸を、前者約1kgに対して後台約1〜1,
5pの割合で混合して骨粉を溶かし、その後加水希釈し
、濾過して骨溶解液を得、一方、鉄乃至銅と硫酸乃至塩
酸を、前者約100gに対して後者的1〜1.5pの割
合で混合し、鉄乃至銅を溶かし、その後加水希釈j7、
濾過して金属溶解液を得、次いで、」−記骨溶解液と金
属溶解液とを、前者lに対して後者的0.3〜0.7の
容量比で混合し均一化する工程を有するものであること
が好ましい。
In the above manufacturing method, calcined and powdered animal bone meal and sulfuric acid or hydrochloric acid are mixed at about 1 to 1 kg per 1 kg of the former.
Bone powder is dissolved by mixing at a ratio of 5p, and then diluted with water and filtered to obtain a bone dissolving solution.Meanwhile, iron or copper and sulfuric acid or hydrochloric acid are mixed at a ratio of 1 to 1.5p of the latter to about 100g of the former. Mix in proportions, dissolve iron to copper, then dilute with water j7,
A metal solution is obtained by filtration, and then the bone solution and the metal solution are mixed and homogenized at a volume ratio of 0.3 to 0.7 for the former to 1 for the latter. Preferably.

(作用) 動物骨粉は、その成分のカルシウムイオン等によって雰
囲気をアルカリ化しつつ、有機物を凝集させる作用をす
る。銅等の溶解した金属は、有機物に馴染みやすく反応
性があり、有機物をより固く凝集させると共に重量を付
加して凝集物を沈降させる作用を有する。
(Function) Animal bone meal has the effect of alkalizing the atmosphere with its components, such as calcium ions, and coagulating organic matter. Dissolved metals such as copper are easily compatible with organic substances and have reactivity, and have the effect of coagulating the organic substances more firmly and adding weight to cause the aggregates to settle.

(実施例) (1)動物骨含有凝集剤について 本発明の凝集剤の原料とする動物骨は、従来畜産場等で
ほとん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。豚、猪等の骨は軟骨が多
く、製造途中の煮沸工程で大部分が溶けてしまうので、
原料として採用するのには適していない。
(Example) (1) About the animal bone-containing flocculant The animal bones used as raw materials for the flocculant of the present invention are mainly bones that were conventionally discarded at livestock farms, especially hard bones of cows, horses, sheep, etc. Animal bones are used. The bones of pigs, boars, etc. have a lot of cartilage, and most of it melts during the boiling process during production.
It is not suitable for use as a raw material.

上記生骨は適度の大きさに切断しつつ、焼成しやすい大
きさにカッティングし、その上で圧力釜(圧縮釜)に投
入し、200〜400℃前後で約90分間前後煮沸する
。次いでこの骨を焼成炉に入れ、900〜1100℃前
後で、60〜180分間前後焼成してから、そのまま炉
内で60分間前後自然冷却させて室温乃至これに近い状
態に戻す。
The above-mentioned raw bones are cut into appropriate sizes and into sizes that are easy to burn, and then put into a pressure cooker (compression cooker) and boiled at about 200 to 400°C for about 90 minutes. Next, the bones are placed in a firing furnace and fired at a temperature of about 900 to 1100°C for about 60 to 180 minutes, and then allowed to naturally cool in the oven for about 60 minutes to return to room temperature or a state close to this temperature.

骨に青成分以外のゼラチン、脂肪、淡白質、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
骨から大刃分離除去することができる。この際、」−記
より明らかに低温又は短時間の煮沸であると、有機物が
充分に除去できず、後の焼成工程に支障を生じさせる。
If organic substances other than the blue component, such as gelatin, fat, white matter, and glue, remain in the bones, they will cause oxidative decay, so it is important to ensure that they are removed. By the boiling process described above, organic substances adhering not only to the outside but also to the inside of the pores can be separated and removed from the bones. At this time, if the boiling is performed at a low temperature or for a short period of time, it is clear from the paragraph "-" that the organic matter cannot be sufficiently removed, causing problems in the subsequent firing step.

上記以上に高温乃至長時間の煮沸条件とする利点は見出
せない。
There is no advantage to using boiling conditions at a higher temperature or for a longer time than the above.

こうして上記煮沸工程で大刀の有機物を除去し、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。煮沸工程無しで焼成するのは、を載物の燃焼と
煙発生が著しく、環境汚染と作業不快、設備損傷を来す
ので、好ましくない。
In this way, by removing the organic matter from the long sword in the boiling process and then passing it through the firing process, it is possible to completely remove the remaining organic matter, and at the same time reduce the humidity (moisture) in the bone.
can be reduced to several percent or less, preferably to almost 0%. Firing without a boiling process is undesirable because it causes significant combustion of the materials and the generation of smoke, which causes environmental pollution, discomfort during work, and damage to equipment.

焼成条件が上記よりも明らかに低い場合は、骨が炭化し
てしまい、また高すぎる場合は骨が灰になってしまい、
いずれの場合も本発明の目的とする機能を発揮しない物
となってしまう。上記条件によれば、骨は白色化して無
数の気孔を存した原形組織状態を維持する。
If the firing conditions are clearly lower than the above, the bones will become carbonized, and if the firing conditions are too high, the bones will turn to ash.
In either case, the product will not function as intended by the present invention. Under the above conditions, the bone becomes white and maintains its original state with numerous pores.

上記焼成冷却後、この骨を破砕しパウダー機にかけて2
0〜200メツシュ前後の骨粉とする。
After the above firing and cooling, the bones are crushed and put into a powder machine for 2
The bone powder should be around 0 to 200 meshes.

上記骨粉は、牛骨の場合は原料の生骨に比して重量比的
40%の収量が得られた。粒子は、カルシウムを主成分
とし、リン、マグネシウム、バリウム、ナトリウム、イ
オウ、カリウム、アルミニウム、鉄、亜鉛、銅、ニッケ
ル等からなっており、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。イオン化はカルシウム等による
アルカリ性である。
In the case of bovine bones, the above-mentioned bone powder yield was 40% by weight compared to raw raw bones. The particles are mainly composed of calcium, phosphorus, magnesium, barium, sodium, sulfur, potassium, aluminum, iron, zinc, copper, nickel, etc., and there are countless microscopic pores communicating inside and outside the particles. ing. Ionization is alkaline due to calcium etc.

而して、上記骨粉と硫酸を、前者約1kgに対して後者
的1〜1.5I!の割合で混合し、約2時間位(又は以
上)をかけて骨粉を溶かし、対硫酸比的8〜12倍(l
)に加水希釈して後、これを濾過して骨溶解液入を得る
Therefore, the amount of the bone powder and sulfuric acid is 1 to 1.5 I for the latter for about 1 kg of the former! The bone powder is mixed at a ratio of 8 to 12 times (l
) and then filtered to obtain an osteolysis solution.

なお、硫酸に代えて塩酸を用いてもよいが、後述する金
属溶解液と混合する場合は、その鉄乃至銅の溶解効率か
らすると硫酸の方が好ましい。
Although hydrochloric acid may be used in place of sulfuric acid, sulfuric acid is preferable in view of its efficiency in dissolving iron and copper when mixed with a metal solution to be described later.

上記骨溶解液Aのみを用いて本発明の動物骨含有凝集剤
とすることができる。
The animal bone-containing flocculant of the present invention can be prepared by using only the above-mentioned osteolytic solution A.

一方、鉄乃至銅と硫酸を、鉄30〜60gと銅40〜7
0gCD混合物に対して後者約1〜1.52の割合で混
合し、約24時間位(又は以上)をかけて鉄及び銅を溶
かし、対硫酸比的8〜12倍(β)に加水希釈して後、
これを濾過して金属溶解液Bを得る。
On the other hand, add iron or copper and sulfuric acid to 30 to 60 g of iron and 40 to 7 g of copper.
Mix the latter at a ratio of about 1 to 1.52 to 0g CD mixture, dissolve iron and copper over about 24 hours (or more), and dilute with water to a ratio of 8 to 12 times (β) relative to sulfuric acid. After that,
This is filtered to obtain metal solution B.

なお、鉄乃至銅は有機物との反応性があり、凝固をより
促進すると共に、凝集物に重さを加えで沈澱しやすくす
る機能を有する。銅の方がより効果があるが、経済性を
有利にするには鉄を混合するのがよい。
Note that iron and copper are reactive with organic substances, and have the function of promoting coagulation and adding weight to aggregates, making them easier to precipitate. Copper is more effective, but for better economics it is better to mix it with iron.

次いで、上記骨溶解液Aと金属溶解液Bとを、前者1に
対して後者約0.3〜0,7の容量比で混合し、混合を
均一にするために80〜120℃好ましくは100℃前
後で、30〜60分前後煮沸し、その後濾過して本発明
の動物骨含有凝集剤を得ることができる。
Next, the bone lysis solution A and the metal lysis solution B are mixed at a volume ratio of about 0.3 to 0.7 of the former to 1, and the mixture is heated at 80 to 120°C, preferably at 100°C, in order to make the mixing uniform. The animal bone-containing flocculant of the present invention can be obtained by boiling at around 30°C for around 30 to 60 minutes and then filtering.

上記凝集剤の主材である骨材は、アルカリイオン化する
ものであることから、上記いずれの動物骨含有凝集剤で
あっても中性乃至アルカリ件領域で効果的に反応する。
Since the aggregate, which is the main material of the flocculant, is alkali ionized, any of the animal bone-containing flocculants mentioned above reacts effectively in the neutral to alkaline range.

そのためにこれを廃水等に使用する場合、pHが酸性領
域の廃水等に対しては、これを中性乃至アルカリ化(7
,0〜9. 5、好ましくは7. 0〜8,5位)する
ために、上記凝集剤と同時にカセイソーダ、或いは硝石
灰等のアルカリ性反応剤を、前者の容量1に対して後者
を0.3〜0.7前後の割合で廃水に混合して使用する
のがよい。なお、廃水等がpH9,5以上と高い場合は
希硫酸等の酸性反応材を用いる。
Therefore, when using this for wastewater, etc., it should be neutralized or alkalined (7
, 0-9. 5, preferably 7. 0 to 8,5), add an alkaline reactant such as caustic soda or nitric lime to the wastewater at the same time as the flocculant at a ratio of 0.3 to 0.7 of the latter to 1 volume of the former. It is best to use a mixture. Note that if the pH of the wastewater or the like is high, such as 9.5 or higher, an acidic reactant such as dilute sulfuric acid is used.

しかし、生活廃水の場合は、塩分、カルンウム等がかな
り混在しているので、上記の如き反応剤4tり加しなく
ても、十分に反応促進する。
However, since domestic wastewater contains a considerable amount of salt, carunium, etc., the reaction can be sufficiently promoted without adding 4 tons of the above-mentioned reactant.

(2)動物骨含有凝集剤による廃水処理について次に、
本発明の動物青金を凝集剤を用いて廃水を処理する方法
及びその装置の例を図面に基づいて説明する。
(2) About wastewater treatment using animal bone-containing flocculants:
An example of the method and apparatus for treating wastewater using an animal flocculant according to the present invention will be explained based on the drawings.

第1図は、一般家庭や一般工場等の通常生活廃水の処理
に好適な処理工程のフローチャート図である。
FIG. 1 is a flowchart of a treatment process suitable for treating wastewater from ordinary households, factories, and the like.

装置には動物骨含有凝集剤Ill、反応剤(カセイソー
ダ又は硝石灰等)槽2を有しており、廃水は、先ず凝集
剤及び反応剤の添加量を調整するための計量槽3に注入
され、次いで攪拌槽4に流入すると同時に反応剤及び動
物骨含有凝集剤が混入され、攪拌機により十分に攪拌さ
れた上で、加圧浮上槽5にコンプレッサによって加圧流
入され有機物をな集浮上させる。上記攪拌W!4は、;
畳拌機付きの凝集剤混和槽4aと攪拌機付きの凝集反応
槽4bとに区画されていてもよい。
The apparatus has a tank 2 for an animal bone-containing flocculant and a reactant (caustic soda or nitric lime, etc.), and the wastewater is first poured into a measuring tank 3 for adjusting the amount of the flocculant and reactant added. Then, at the same time as it flows into the stirring tank 4, a reactant and an animal bone-containing flocculant are mixed in, sufficiently stirred by a stirrer, and then flowed under pressure by a compressor into a pressurized flotation tank 5 to collect and float organic matter. Stir above! 4 is;
It may be divided into a flocculant mixing tank 4a with a folding stirrer and a flocculation reaction tank 4b with a stirrer.

該加圧浮JJJ5の土兄に配設されたスキマーを通った
処理水は濾過槽6に流入されろ。上記加圧浮上槽5内で
加圧浮上した凝集物は、スキマーによって分離された後
スラッジ禮に吸引ざね、スラッジとして堆債させる。
The treated water that has passed through the skimmer installed at the bottom of the pressurized float JJJ5 flows into the filtration tank 6. The aggregates floated under pressure in the pressurized flotation tank 5 are separated by a skimmer and then sucked into a sludge tray to be deposited as sludge.

濾過槽6は細かい砂を積層させたものであってもよく、
本発明の方法によって焼成したSjJ物骨の細片、或い
は該動物骨を粉状化したものと粘土扮とを練り合わせて
粒状化して焼成した動物骨含有粒体を積層させたもので
あってもすい。前者の濾過層によれば、有機物除去後の
細かい不純物を除去できるので、一般廃水には充分に対
応できる。
The filter tank 6 may be made of layered fine sand,
SJJ bone fragments fired by the method of the present invention, or animal bone-containing granules made by kneading the pulverized animal bones and clay, granulating them, and firing them, are laminated. water. The former filtration layer can remove fine impurities after organic matter has been removed, so it can be used satisfactorily for general wastewater.

後者の濾過層によれば、該不純物の除去に加えて骨のア
ルカリイオン化による処理水のアルカリ化とミネラル化
が行われるので、有機物汚染度の比較的高い廃水等に特
に効果的である。
The latter filtration layer not only removes the impurities but also alkalinizes and mineralizes the treated water by alkali ionization of the bones, so it is particularly effective for wastewater with a relatively high degree of organic contamination.

上記処理水は、無味無臭であって、そのまま放流しても
環境汚染のおそれはなく、洗浄用水等として充分に再利
用が可能である。また上記処理水を別配管を通して濾過
槽内に強制逆流させる機構を採用ずれば、濾過槽内の自
動洗浄が可能である。
The above-mentioned treated water is tasteless and odorless, and there is no risk of environmental pollution even if it is discharged as it is, and it can be fully reused as water for washing or the like. Furthermore, if a mechanism is adopted in which the treated water is forced to flow back into the filtration tank through a separate pipe, automatic cleaning of the inside of the filtration tank is possible.

第2図は、屠殺場廃水、畜産加工場廃水、汚物廃水等の
如き腐敗性有機物を含む汚染度の高い廃水処理に好適な
処理工程のフローチャート図である。
FIG. 2 is a flowchart of a treatment process suitable for treating highly contaminated wastewater containing perishable organic matter, such as slaughterhouse wastewater, livestock processing plant wastewater, filth wastewater, and the like.

先ず、屠殺場等から直接排出されろ廃水は、自動スクリ
ーンを通して調整槽11に導入され、固形分等のうち粒
子の大きい不純物を除去されて貯液される(以下これを
廃水と言う)、、廃水は、単位時間あたりに処理可能な
流を及び流速を調整する計量噴12を通し2で混和槽1
3、反応槽14に導入される。両槽にはいずれも攪拌羽
恨が又聞されていると共に、カセイソーダ乃至硝石灰等
の反応剤注入袋715、本発明に係るD物青金有訂集剤
注入装百16が連設みれており、廃水のp Hが7゜0
−=9.5の範囲内となるように反応剤が注入され、廃
水の濃度(生物化学的酸素供給1(BODを測定基準と
した場合)に応じて廃水に対してごく少債の動物骨含有
凝集剤が注入される。例えばBOD800(W度の廃;
k 1 m’に対して、約215ccの動物骨含有凝集
剤が注入され、順次1〜5分程度攪拌混和されろ。
First, wastewater directly discharged from a slaughterhouse, etc. is introduced into the adjustment tank 11 through an automatic screen, where large-particle impurities such as solids are removed and stored (hereinafter referred to as wastewater). The wastewater is passed through a metering jet 12 that adjusts the flow rate and the flow rate that can be processed per unit time, and is then transferred to a mixing tank 1.
3. Introduced into reaction tank 14. In both tanks, stirring is also heard, and a bag 715 for injecting a reactant such as caustic soda or nitric lime, and a device for injecting a D-type blue gold collection agent according to the present invention are also installed in series. The pH of the wastewater is 7°0.
- = 9.5, the reactant is injected so that the concentration of the wastewater (biochemical oxygen supply 1 (BOD as the measurement standard) Containing flocculant is injected.For example, BOD800 (W degree waste;
Approximately 215 cc of animal bone-containing flocculant is injected into k 1 m', and the mixture is sequentially stirred and mixed for about 1 to 5 minutes.

」1記廃水は、次に加圧浮七搏17に下部からコンプレ
ッサによる加圧を受けて導入され、加圧によって浮上し
た凝集物を−L方に配設されたスキマーによって分離し
て、次の第2反応槽18に流出される。3J:方に浮上
しスキマーによって分離された凝集物は汚泥濃縮槽31
に排出される。
The wastewater described in item 1 is then introduced from the lower part of the pressurized float 17 under pressure by a compressor, and the aggregates that float to the surface due to the pressure are separated by a skimmer disposed on the -L side, and the following is carried out. It is discharged into the second reaction tank 18. 3J: The flocs that float to the side and are separated by the skimmer are sent to the sludge thickening tank 31.
is discharged.

第2反応槽18には、再度動物骨含有凝集剤注入装置1
9、及びpH調整のため必要に応じて反応剤注入装置2
0からそれぞれ必要9の注入を受けて攪拌反応されて凝
集沈殿槽21に移送され、前記加圧浮上fH7で分離し
きれなかった残存有機物が凝縮沈澱される。該沈澱物は
前記汚泥a縮槽31に排出される。処理水はフィルター
を通して貯液槽22に一端貯液された後、砂を濾材とし
て積層した縦長の濾過槽23に一定流量で移送され、該
濾過槽23を自然流下した後、貯液槽24に貯液される
。25は、濾材として本発明に係る方法で焼成した動物
骨の細片、又は該動物骨をパウダー化した骨粉とつなぎ
材としての粘土を焼成ハウダー化した粘土粉とを混練、
造粒化した動物骨主体の粒体を積層l、7てなる縦長の
濾過槽である。
The second reaction tank 18 is again filled with the animal bone-containing flocculant injection device 1.
9, and a reactant injection device 2 as necessary for pH adjustment.
Required amounts of 9 are injected from 0 to 9, stirred and reacted, and transferred to a flocculation-sedimentation tank 21, where the remaining organic matter that could not be completely separated by the pressure flotation fH7 is condensed and precipitated. The precipitate is discharged to the sludge aggregation tank 31. The treated water passes through a filter and is temporarily stored in a liquid storage tank 22, and then transferred at a constant flow rate to a vertically long filtration tank 23 in which sand is layered as a filter medium. The liquid is stored. 25 is a method of kneading small pieces of animal bone fired by the method according to the present invention as a filter medium, or bone powder obtained by turning the animal bone into powder, and clay powder obtained by turning clay into a fired howder as a binder;
This is a vertically elongated filtration tank consisting of 1 and 7 layers of granulated animal bone-based granules.

貯液槽24の処理水は濾過槽25に一定流量で移送され
、自然流下して、殺菌装置2Gから(”l○2の添加を
受け、殺菌処理されて処理水槽27に貯水される。各濾
過槽23.25はいずれも残存した微小不純物を除去V
るものであり、濾過槽25はカルシウム等の骨の成分に
より処理水をアルカリイオン化しミネラル水とする作用
も有してい処理水槽27には逆洗性用ブロア28を配管
接続j7、処理水を両濾過槽23.25に強制逆流入さ
せ、濾過槽内を処理水が逆流して洗浄する機能を設けれ
ば、濾過槽を長期的機能低下させずに維持することがで
きる。また、処理水槽27には再生水ポンプ29を配管
接続し、処理水を屠殺場等の洗浄水その他に再利用する
ことができる。もとよりそのまま放流しても環境汚染の
おそれはない。
The treated water in the liquid storage tank 24 is transferred to the filtration tank 25 at a constant flow rate, flows down naturally, receives the addition of (1○2) from the sterilizer 2G, is sterilized, and is stored in the treated water tank 27. Both filtration tanks 23 and 25 remove remaining minute impurities.
The filter tank 25 also has the function of alkaline ionizing the treated water using bone components such as calcium and turning it into mineral water.A backwashing blower 28 is connected to the pipe j7 to the treated water tank 27, and the treated water is If a function is provided in which the treated water is forced to flow back into both the filtration tanks 23 and 25 and the treated water flows back into the filtration tank for cleaning, the filtration tank can be maintained over a long period of time without deteriorating its function. Furthermore, a reclaimed water pump 29 is connected to the treated water tank 27 via piping, so that the treated water can be reused as washing water for slaughterhouses, etc. There is no risk of environmental pollution even if it is released as is.

なお、従来の活性汚泥法等による廃水処理設備に上記本
発明に係る装置を組み合わせろ場合は、従来装置30の
最終沈澱槽から放流される処理水を第2反応槽18に導
入し、その後の」1記処理工程を通るようにするのがよ
い。
In addition, when combining the apparatus according to the present invention with a conventional wastewater treatment facility using the activated sludge method, etc., the treated water discharged from the final settling tank of the conventional apparatus 30 is introduced into the second reaction tank 18, and the subsequent It is preferable to pass through the processing steps described in 1.

汚泥濃縮槽31に集積されたスラッジは、a$1された
後、汚泥処理工程を経て適度に乾燥され、適宜に廃棄さ
れ、或いは造粒ニー程を経て後自然醗酵させて、肥料又
は土壌改良材として使用することができる。上記スラッ
ジは前記有機物の堆積であるので、天然肥料又は土壌改
良材として優れた効能を発揮する。
The sludge accumulated in the sludge thickening tank 31 is made into a sludge, and then subjected to a sludge treatment process, dried appropriately, and disposed of appropriately, or passed through a granulation knee process, and then naturally fermented to be used as fertilizer or soil improvement. It can be used as a material. Since the sludge is a deposit of the organic matter, it exhibits excellent efficacy as a natural fertilizer or soil conditioner.

実験例1 熊本県所在の成る食肉センター(屠殺場)から排出され
た未処理廃水(以下原水という)八と、該原水を該会社
に設置され現運転中の一般的活性汚泥処理装置によって
処理された処理水Bと、該原水を第2図に示した本発明
に係る工程を経て処理した処理水Cとを、社団法人熊本
県薬剤師会医薬品検査センターで分析した結果は、表1
に示すとおりであった。
Experimental Example 1 Untreated wastewater (hereinafter referred to as raw water) discharged from a meat center (slaughterhouse) located in Kumamoto Prefecture was treated with a general activated sludge treatment equipment installed at the company and currently in operation. Table 1 shows the results of analysis of treated water B and treated water C, which was obtained by processing the raw water through the process according to the present invention shown in Figure 2, at the Pharmaceutical Testing Center of the Kumamoto Prefectural Pharmacists Association.
It was as shown in .

表1 BODは生物化学的酸素消費量、CODは化学的酸素消
費量、SSはl!!!濁物質である。分析方法は、上記
分析項目の上から順に規IN2.1、m境庁告示第:〕
9号、規格17、規格21.厚生省建設省令第1号、環
境庁告示第64号付表によった。
Table 1 BOD is biochemical oxygen consumption, COD is chemical oxygen consumption, SS is l! ! ! It is a cloudy substance. The analysis method is as follows from the top of the above analysis items: Regulation IN 2.1, Boundary Office Notification No.:]
No. 9, Standard 17, Standard 21. According to Ministry of Health, Labor and Welfare, Construction Ministry Ordinance No. 1 and Environment Agency Notification No. 64 Appendix.

規格はJISKO102である。The standard is JISKO102.

実験例2 鹿児島県所在の成る食肉加工場(屠殺場)から排出され
た原水へと、該原水を第2図に示した本発明に係る工程
を経て処理した処理水Cとを、財団法人鹿児島県公害防
止協会で分析した結果は、表2に示すとおりであった。
Experimental Example 2 Raw water discharged from a meat processing plant (slaughterhouse) located in Kagoshima Prefecture was treated with treated water C through the process according to the present invention shown in Fig. The results of the analysis conducted by the Prefectural Pollution Control Association are shown in Table 2.

表  2 1 pHl  6.0   8.41 分析方法は実験例1と同じである。Table 2 1 pHl 6.0 8.41 The analysis method was the same as in Experimental Example 1.

実験例:3 北九州市所在の成る食肉センター(屠殺場)から排出さ
れた原水へと、該原水を該会社に設置され現運転中の一
般的活性汚泥処理装置によって処理された処理水Bと、
該原水を第2図に示した本発明に係る工程を経て処理し
た処理水Cとを、財団法人北九州市環境整備協会で分析
した結果は、表3に示すとおりであった。
Experimental example: 3 Raw water discharged from a meat center (slaughterhouse) located in Kitakyushu City was treated with treated water B by a general activated sludge treatment equipment installed at the company and currently in operation.
The treated water C obtained by treating the raw water through the process according to the present invention shown in FIG. 2 was analyzed by the Kitakyushu City Environmental Improvement Association, and the results are shown in Table 3.

表  3 分析方法は、3SがJ l5KO102141で、他は
実験例1と同じである。
Table 3 The analysis method was the same as in Experimental Example 1 except that 3S was J15KO102141.

実験例4 福岡県所在の成る食肉加工場(屠殺場〉から排出された
原水へと、該原水を第2図に示した本発明に係る工程を
経で処理した処理水Cとを、財団法人日本環境衛生セン
ターで分析した結果は、表4に示すとおりであった。
Experimental Example 4 Raw water discharged from a meat processing plant (slaughterhouse) located in Fukuoka Prefecture was treated with treated water C through the process according to the present invention shown in Figure 2. The results of the analysis at the Japan Environmental Health Center were as shown in Table 4.

表  4 ■ IC0r)+−、’ 420mg/l   5,8 1
分析方法は、大腸菌群数がMPN法、他は実験例1と同
じである。
Table 4 ■ IC0r)+-,' 420mg/l 5,8 1
The analysis method was the same as in Experimental Example 1 except for the MPN method for the number of coliform bacteria.

実験例5 宮崎県所在の成るにわとり処理(ブロイラー)会社から
排出された原水Aと、該原水を該会社に設置され現運転
中の一般的活性汚泥処理装置によ、って処理された処理
水Bど、該原水を第2図に示した本発明に係る工程を経
て処理した処理水Cとを、財団法人宮崎県公害防止管理
協会で分析した結果は、表5に示すとおりであった。
Experimental Example 5 Raw water A discharged from a chicken processing (broiler) company located in Miyazaki Prefecture, and treated water treated by treating the raw water with a general activated sludge treatment equipment installed at the company and currently in operation. Table 5 shows the results of analysis of treated water B and treated water C, which were treated through the process according to the present invention shown in FIG. 2, by the Miyazaki Prefecture Pollution Prevention and Management Association.

表  5 分析方法は、上記分析項目の上から5項目までは実験例
1と同じ。末項目は環境庁告示第59号付表7によった
Table 5 The analysis method is the same as in Experimental Example 1 for the top five analysis items above. The last item is based on Appendix Table 7 of Environment Agency Notification No. 59.

実験例6 従来、水道水の消毒は次亜塩素酸ソーダにより、BOD
、CODの処理は硫酸バンド−1,二より、S5の処理
は活性炭により行っていた。この水道用取水に本発明に
係る凝集剤を添加(取水1 m+について20cc程度
)シ、たところ、有機物等の凝集が顕著であり、各検査
項目についての数位は、上記従来の処理後の浄水に比し
て数10−数100分の−に減少し、特にCODに”つ
(ど、′の減少が著しかった。従来の浄水に本発明に係
る凝集剤を添加したところ、やはり有機物等の凝集が目
視状餌でも明確に表れた。
Experimental Example 6 Conventionally, tap water was disinfected using sodium hypochlorite, which caused BOD
, COD treatment was performed using sulfuric acid bands 1 and 2, and S5 treatment was performed using activated carbon. When the flocculant according to the present invention was added to this water intake for tap water (approximately 20 cc per 1 m+ of water intake), the flocculation of organic matter was remarkable, and the numbers for each inspection item were higher than that of the purified water after the above conventional treatment. The reduction in COD was particularly remarkable.When the flocculant of the present invention was added to conventional water purification, the amount of organic matter, etc. Aggregation was clearly visible even in visually observed baits.

なお、上記いずれの実験例においても、試料Aは強い生
ぐさ臭を発りでおり、試料Bは弱腐敗臭があったが、試
料Cはほとんど臭気が感じられなか、った。また、試料
Cは無色透明であった。
In all of the above experimental examples, sample A gave off a strong raw odor, sample B had a weak rotten odor, but sample C had almost no odor. Moreover, Sample C was colorless and transparent.

試料Cは高い浄化力によって飲料としてもよいほどに再
生されており、これを2(]人が試飲してみた結果は、
全てが水道水よりも軽く甘味のあるいわゆる天然ミネラ
ル水と同様な感覚を得た。
Sample C has been regenerated to the extent that it can be used as a drink due to its high purifying power, and the results of two people tasting it are as follows:
Everything felt lighter and sweeter than tap water, similar to so-called natural mineral water.

以上から明らかなように、P、記装置による再生水を工
場用水、或いは洗浄用水の外、各種用水として使用した
場合は、使用後の水を再びF記装置によって浄化すれば
、何度でも再生水として利用することができ、水の省資
源に役立つ。
As is clear from the above, when the recycled water produced by the device described in P and above is used as factory water or water for various purposes other than water for washing, if the water after use is purified again by the device described in F, it can be used as recycled water any number of times. It can be used to help conserve water resources.

なお、を記処理によって分離された凝集物は、有機物で
あるため、適当な処理を加えることで肥料や堆肥として
利用することができる。
Since the aggregates separated by the above treatment are organic substances, they can be used as fertilizer or compost by applying appropriate treatment.

〈発明の効果) 以」−のように、本発明によれば、従来活用法もゾよく
大力廃棄処分していた動物骨を活用し、簡単な方法で、
動物骨含有凝集剤を製造することができる。この凝集剤
によれば、−次的濾過によって比較的大きな固形物を除
去した後、凝縮反応を十分に行わせることによって、廃
水、特に動物性等の腐敗性有機物を含む廃水を浄化する
と同時にミネラル化し、飲用可能な程度まで水質を浄化
した再生水を得ることができ、その処理を比較的短時間
に可能とし、しかもそのための装置を比較的簡屯な構造
で安価なものとし、メンテナンスの容易なものとするこ
とができる。
<Effects of the Invention> As stated above, according to the present invention, animal bones, which were conventionally disposed of in a very large manner, can be used in a simple manner.
Animal bone-containing flocculants can be produced. According to this flocculant, after relatively large solids are removed through secondary filtration, a condensation reaction is sufficiently carried out to purify wastewater, especially wastewater containing putrefactive organic matter such as animal matter, and at the same time remove minerals. It is possible to obtain reclaimed water whose quality has been purified to a drinkable level, which can be treated in a relatively short period of time, and the equipment for this purpose has a relatively simple structure and is inexpensive, and it is easy to maintain. can be taken as a thing.

動物骨溶解液だけの構成の凝集剤によれば、凝集物を分
離するだめのフィルター等による分離作業が不可欠であ
るが、鉄、銅等の金属溶解液を混合した構成の凝集剤に
よれば、凝集物は凝固沈殿するので、分離作業を容易に
する。
If a flocculant is made up of only an animal bone solution, it is necessary to use a filter to separate the aggregates, but if a flocculant is mixed with a solution of metals such as iron or copper, , the aggregates coagulate and precipitate, making the separation process easier.

本発明に係る凝集剤によって浄化された再生水は、広範
囲での再刊用に適している外、自然水域に放流しても汚
濁の危険性がない。
Reclaimed water purified by the flocculant according to the present invention is not only suitable for reprinting over a wide range of areas, but also poses no risk of contamination even when discharged into natural water bodies.

また、本発明によって得られた再生水を使用した場合は
、使用後の水を再び本発明によって浄化すれば、何度で
も再生水として利用することができ、水の省資源に役立
つ。
Moreover, when the recycled water obtained by the present invention is used, if the water after use is purified again by the present invention, it can be used as recycled water any number of times, which is useful for saving water resources.

【図面の簡単な説明】[Brief explanation of the drawing]

第1図は本発明に係る凝集剤を用いた廃水処理の一例を
示す70−チャート図、第2図は同様廃水処理の別の一
例を示すフローチア−1図である。 1.16・・動物骨含有凝集剤槽、2.15・・・中和
剤槽、3,12・・・計量槽、4a、13・・・混和槽
、4b、14・・・反応槽、5,17・・・加圧浮上槽
、6゜23.25・・・濾過槽、 出廓人  俵  1) 佐  内 手続補正書妨式)屯 昭和63年 7月29日 特許庁長官  吉 1)文 毅  殿 1、事件の表示 昭和63年 特許軸 第105580
号2、発明の名称  動物骨含有凝集剤及びその製造、
使用方法藤田佐内 ↓ (JILEI!水)
FIG. 1 is a 70-chart diagram showing an example of wastewater treatment using the flocculant according to the present invention, and FIG. 2 is a flowchart diagram 1 showing another example of the same wastewater treatment. 1.16... Animal bone-containing flocculant tank, 2.15... Neutralizing agent tank, 3, 12... Measuring tank, 4a, 13... Mixing tank, 4b, 14... Reaction tank, 5, 17... Pressurized flotation tank, 6゜23.25... Filtration tank, shipping person bales 1) Certification of internal procedural amendments) Tun July 29, 1988 Director General of the Japan Patent Office Yoshi 1) Moon Yi 1, Incident Display 1986 Patent Axis No. 105580
No. 2, Title of the invention: Animal bone-containing flocculant and production thereof;
How to use Sanai Fujita↓ (JILEI!Wednesday)

Claims (6)

【特許請求の範囲】[Claims] (1)焼成粉状化された動物骨粉を硫酸又は塩酸に溶か
してなる骨溶解液からなる動物骨含有凝集剤。
(1) An animal bone-containing flocculant consisting of an osteolytic solution prepared by dissolving calcined powdered animal bone powder in sulfuric acid or hydrochloric acid.
(2)焼成粉状化された動物骨粉を硫酸又は塩酸に溶か
してなる骨溶解液と、鉄乃至銅を硫酸又は塩酸に溶かし
てなる金属溶解液とが均一に混合されてなる動物骨含有
凝集剤。
(2) Animal bone-containing aggregate made by uniformly mixing a bone dissolving solution made by dissolving calcined powdered animal bone powder in sulfuric acid or hydrochloric acid, and a metal dissolving solution made by dissolving iron or copper in sulfuric acid or hydrochloric acid. agent.
(3)焼成粉状化された動物骨粉と硫酸又は塩酸を混合
した上で骨溶解液を得、一方、鉄乃至銅と硫酸乃至塩酸
を混合した上で金属溶解液を得、その上で両液を混合一
体化することを特徴とする動物骨含有凝集剤の製造方法
(3) A bone solution is obtained by mixing calcined powdered animal bone powder with sulfuric acid or hydrochloric acid, and a metal solution is obtained by mixing iron or copper with sulfuric or hydrochloric acid, and then both A method for producing an animal bone-containing flocculant, which comprises mixing and integrating liquids.
(4)焼成粉状化された動物骨粉と硫酸又は塩酸を、前
者約1kgに対して後者約1〜1.5lの割合で混合し
て骨粉を溶かし、その後加水希釈し、濾過して骨溶解液
を得、一方、鉄乃至銅と硫酸乃至塩酸を、前者約100
gに対して後者約1〜1.5lの割合で混合し、鉄乃至
銅を溶かし、その後加水希釈し、濾過して金属溶解液を
得、次いで、上記骨溶解液と金属溶解液とを、前者1に
対して後者約0.3〜0.7の容量比で混合し均一化す
る工程を有する動物骨含有凝集剤の製造方法。
(4) Mix the calcined powdered animal bone powder with sulfuric acid or hydrochloric acid at a ratio of about 1 to 1.5 liters of the latter to about 1 kg of the former to dissolve the bone powder, then dilute with water, filter, and dissolve the bone. On the other hand, iron to copper and sulfuric acid to hydrochloric acid were added at about 100%
The latter is mixed at a ratio of about 1 to 1.5 liters per g to dissolve iron or copper, then diluted with water and filtered to obtain a metal solution, and then the bone solution and metal solution are mixed together. A method for producing an animal bone-containing flocculant comprising the step of mixing and homogenizing the former at a volume ratio of 1 to the latter at a volume ratio of about 0.3 to 0.7.
(5)焼成粉状化された動物骨粉を硫酸又は塩酸に溶か
してなる骨溶解液からなる動物骨含有凝集剤を、処理液
にアルカリ性反応材を添加した上で添加使用することを
特徴とする動物骨含有凝集剤の使用方法。
(5) An animal bone-containing flocculant consisting of an osteolytic solution obtained by dissolving calcined powdered animal bone powder in sulfuric acid or hydrochloric acid is used after adding an alkaline reactive material to the treatment solution. How to use animal bone-containing flocculants.
(6)焼成粉状化された動物骨粉を硫酸又は塩酸に溶か
してなる骨溶解液と、鉄乃至銅を硫酸又は塩酸に溶かし
てなる金属溶解液とが均一に混合されてなる動物骨含有
凝集剤を、処理液にアルカリ性反応材を添加した上で添
加使用することを特徴とする動物骨含有凝集剤の使用方
法。
(6) Animal bone-containing aggregate made by uniformly mixing a bone dissolving solution made by dissolving calcined powdered animal bone powder in sulfuric acid or hydrochloric acid, and a metal dissolving solution made by dissolving iron or copper in sulfuric acid or hydrochloric acid. 1. A method of using an animal bone-containing flocculant, which comprises adding the agent to a treatment solution after adding an alkaline reactive material thereto.
JP10558088A 1988-04-28 1988-04-28 Coagulant containing animal bone, and its production and using the coagulant Granted JPH01274807A (en)

Priority Applications (8)

Application Number Priority Date Filing Date Title
JP10558088A JPH01274807A (en) 1988-04-28 1988-04-28 Coagulant containing animal bone, and its production and using the coagulant
CA 584061 CA1335153C (en) 1988-04-28 1988-11-24 Activating material composed mainly of animal bone, flocculating agent composed mainly of the material and processes for preparation thereof
US07/276,265 US5047255A (en) 1988-04-28 1988-11-25 Activating material composed mainly of animal bone, flocculating agent composed mainly of the material and processes for preparation thereof
NZ22709388A NZ227093A (en) 1988-04-28 1988-11-25 Activating material comprising calcined bone; flocculating agents
AU25911/88A AU623613B2 (en) 1988-04-28 1988-11-25 Activating material composed mainly of animal bone, flocculating agent composed mainly of the material and processes for preparation thereof
US07/756,809 US5254285A (en) 1988-04-28 1991-09-09 Flocculating agent for the purification of fluids
US08/088,160 US5397499A (en) 1988-04-28 1993-07-07 Alkali-ionization and oxidation inhibiting composition
US08/373,004 US5487844A (en) 1988-04-28 1995-01-17 Flocculating agent for the purification of fluids

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP10558088A JPH01274807A (en) 1988-04-28 1988-04-28 Coagulant containing animal bone, and its production and using the coagulant

Publications (2)

Publication Number Publication Date
JPH01274807A true JPH01274807A (en) 1989-11-02
JPH0553521B2 JPH0553521B2 (en) 1993-08-10

Family

ID=14411444

Family Applications (1)

Application Number Title Priority Date Filing Date
JP10558088A Granted JPH01274807A (en) 1988-04-28 1988-04-28 Coagulant containing animal bone, and its production and using the coagulant

Country Status (1)

Country Link
JP (1) JPH01274807A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006524537A (en) * 2003-03-12 2006-11-02 スリーエム イノベイティブ プロパティズ カンパニー POLYMER COMPOSITION, MEDICAL ARTICLE, AND METHOD CONTAINING BIOLOGICALLY ACTIVE SILVER, COPPER OR ZINC COMPOUND
WO2007074758A1 (en) * 2005-12-26 2007-07-05 Eccera Co., Ltd. Flocculating agent
JP2012250225A (en) * 2011-06-07 2012-12-20 Horibe Yoshikazu Method for treating palm waste oil
JP5492335B1 (en) * 2013-08-08 2014-05-14 株式会社ケイ・アール・ジー Method for producing flocculant and flocculant
JP2019037955A (en) * 2017-08-28 2019-03-14 水ing株式会社 Water treatment method of oil-containing waste water, and water treatment apparatus of oil-containing waste water

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2006524537A (en) * 2003-03-12 2006-11-02 スリーエム イノベイティブ プロパティズ カンパニー POLYMER COMPOSITION, MEDICAL ARTICLE, AND METHOD CONTAINING BIOLOGICALLY ACTIVE SILVER, COPPER OR ZINC COMPOUND
WO2007074758A1 (en) * 2005-12-26 2007-07-05 Eccera Co., Ltd. Flocculating agent
JPWO2007074758A1 (en) * 2005-12-26 2009-06-04 株式会社エクセラ Flocculant
US7666311B2 (en) 2005-12-26 2010-02-23 Eccera Co., Ltd. Flocculating agent
AU2006329317B2 (en) * 2005-12-26 2010-09-30 Eccera Co., Ltd. Flocculating agent
JP2012250225A (en) * 2011-06-07 2012-12-20 Horibe Yoshikazu Method for treating palm waste oil
JP5492335B1 (en) * 2013-08-08 2014-05-14 株式会社ケイ・アール・ジー Method for producing flocculant and flocculant
JP2019037955A (en) * 2017-08-28 2019-03-14 水ing株式会社 Water treatment method of oil-containing waste water, and water treatment apparatus of oil-containing waste water

Also Published As

Publication number Publication date
JPH0553521B2 (en) 1993-08-10

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