JPH0553521B2 - - Google Patents

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Publication number
JPH0553521B2
JPH0553521B2 JP10558088A JP10558088A JPH0553521B2 JP H0553521 B2 JPH0553521 B2 JP H0553521B2 JP 10558088 A JP10558088 A JP 10558088A JP 10558088 A JP10558088 A JP 10558088A JP H0553521 B2 JPH0553521 B2 JP H0553521B2
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JP
Japan
Prior art keywords
animal bone
bone
sulfuric acid
dissolving
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.)
Expired - Lifetime
Application number
JP10558088A
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Japanese (ja)
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JPH01274807A (en
Inventor
Sanai Fujita
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
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Individual
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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 AU25911/88A priority patent/AU623613B2/en
Priority to NZ22709388A priority patent/NZ227093A/en
Priority to US07/276,265 priority patent/US5047255A/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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Description

【発明の詳細な説明】[Detailed description of the invention]

(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。 (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、硫酸バンドー、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。 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。
活性汚泥法によつた処理水は、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。 (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つた。 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。 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、これによつ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つた。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
不適であつた。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
力も過大であつた。 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
法とは異なつて、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せんと
する目的をも持つものである。 (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を、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、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であ
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凝集剤
の使用方法にある。 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
者約1〜1.5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
対して約1〜1.5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ものであることが好まし
い。 (作用) 動物骨粉は、その成分のカルシウムイオン等に
よつ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。 (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。 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ツテングし、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。 骨に骨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。上記煮沸工程によつて、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。この際、上記よ
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。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。 こうして上記煮沸工程で大方の有機物を除去
し、その上で上記焼成工程を通すことによつ
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、有機物の燃
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。 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
灰になつてしまい、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つてしまう。
上記条件によれば、骨は白色化して無数の気孔
を有した原形組織状態を維持する。 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メツシユ前後の骨粉とする。 上記骨粉は、牛骨の場合は原料の生骨に比し
て重量比約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、ニツケル等からな
つており、粒子の内外に渡つて無数の微小気孔
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。 而して、上記骨粉と硫酸を、前者約1Kgに対
して後者約1〜1.5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
酸比約8〜12倍()に加水希釈して後、これ
を濾過して骨溶解液Aを得る。 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。 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。 一方、鉄乃至銅と硫酸を、鉄30〜60gと銅40
〜70gの混合物に対して後者約1〜1.5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、対硫酸比約8〜12倍()
に加水希釈して後、これを濾過して金属溶解液
Bを得る。 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
えて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、経済性を有利するには鉄を
混合するのがよい。 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。 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つても中性乃至アルカリ
性領域で効果的に反応する。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。 しかし、生活廃水の場合は、塩分、カルシウ
ム等がかなり混在しているので、上記の如き反
応剤を添加しなくても、十分に反応促進する。 (2) 動物骨含有凝集剤による廃水処理について 次に、本発明の動物骨含有凝集剤を用いて廃
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。 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ヤート
図である。 装置には動物骨含有凝集剤槽1、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、次いで撹拌槽
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、撹拌機により十分に撹拌され
た上で、加圧浮上槽5にコンプレツサによつて
加圧流入され有機物を凝集浮上させる。上記撹
拌槽4は、撹拌機付きの凝集剤混和槽4aと撹
拌機付きの凝集反応槽4bとに区画されていて
もよい。 該加圧浮上槽5の上部に配設されたスキマー
を通つた処理水は濾過槽6に流入される。上記
加圧浮上槽5内で加圧浮上した凝集物は、スキ
マーによつて分離された後スラツジ槽に吸引さ
れ、スラツジとして堆積させる。 濾過槽6は細かい砂を積層させたものであつ
てもよく、本発明の方法によつて焼成した動物
骨の細片、或いは該動物骨を粉状化したものと
粘土粉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つてもよ
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。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。 上記処理水は、無味無臭であつて、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
せる機構を採用すれば、濾過槽内の自動洗浄が
可能である。 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ヤート
図である。 先ず、屠殺場等から直接排出される廃水は、
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、単位時間あたり処理可能な流量及び流
速を調整する計量槽12を通して混和槽13、
反応槽14に導入される。両槽にはいずれも撹
拌羽根が装置されていると共に、カセイソーダ
乃至硝石灰等の反応剤注入装置15、本発明に
係る動物骨含有凝集剤注入装置16が連設され
ており、廃水のPH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
的酸素供給量BODを測定基準とした場合)に
応じて廃水に対してごく少量の動物骨含有凝集
剤が注入される。例えばBOD800程度の廃水1
m3に対して、約25c.c.の動物骨含有凝集剤が注入
され、順次1〜5分程度撹拌混和される。 上記廃水は、次に加圧浮上槽17に下部から
コンプレツサによる加圧を受けて導入され、加
圧によつて浮上した凝集物を上方に配設された
スキマーによつて分離して、次の第2反応槽1
8に流出される。上方に浮上しスキマーによつ
て分離された凝集物は汚泥濃縮槽31に排出さ
れる。 第2反応槽18には、再度動物骨含有凝集剤
注入装置19、及びPH調整のため必要に応じて
反応剤注入装置20からそれぞれ必要量の注入
を受けて撹拌反応されて凝集沈澱槽21に移送
され、前記加圧浮上槽17で分離しきれなかつ
た残存有機物が凝縮沈澱される。該沈澱物は前
記汚泥濃縮槽31に排出される。処理水はフイ
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
層してなる縦長の濾過槽である。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26からClO2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
小不純物を除去するものであり、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をする作用も有してい
る。 処理水槽27には逆洗浄用ブロア28を配管
接続し、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。 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る場合
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、その後の上
記処理工程を通るようにするのがよい。 汚泥濃縮槽31に集積されたスラツジは、濃
縮された後、汚泥処理工程を経て過度に乾燥さ
れ、適宜に廃棄され、或いは造粒工程を経て後
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。上記スラツジは前記有機
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。 実験例 1 熊本県所在の或る食肉センター(屠殺場)から
排出された未処理廃水(以下原水という)Aと、
該原水を該会社に設置され現運転中の一般的活性
汚泥装置装置によつ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
とおりであつた。
(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. (Prior art) Bando sulfate, aluminum chloride polymer,
Ferric chloride etc. are present. 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. (Problem to be solved by the invention) However, since all of the above conventional flocculants react on the acidic side, the treated water must become acidic, and the problem of environmental pollution due to discharge remains. Ta. Moreover, the above-mentioned flocculant did not react with general public tap water or water with a low degree of contamination, but functioned with considerably contaminated wastewater. 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. On the other hand, in the conventional activated sludge method, when wastewater containing putrefactive organic matter such as animal products is treated with this activated sludge method, the quality of the treated water obtained by this method satisfies the standard value that can be discharged. In Although,
PH is acidic, BOD and COD are both around 30 to 60 ppm,
The water quality could not necessarily be said to be sufficient in terms of being harmless to natural water bodies, such as odor not being completely removed. Moreover, 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. Further, complex and large-scale equipment is required, and the equipment cost is large, and maintenance costs and labor are also excessive. Therefore, unlike the conventional activated sludge method that uses microorganisms such as bacteria to separate impurities from wastewater, the present invention can be used as a simple means of setting conditions, and is easy to use and maintain on a small scale. This method deodorizes, sterilizes, and purifies wastewater, especially wastewater containing putrefactive organic matter such as animal matter, in a short period of time, producing recycled water with a quality equal to or better than that of tap water, and does not cause pollution even when released into natural water bodies. The purpose of the present invention is to provide an animal bone-containing flocculant particularly suitable for wastewater treatment, which not only does not pose a risk of wastewater, but also produces reclaimed water suitable for wide-scale reuse, thereby enabling efficient wastewater treatment. It also has. (Means for Solving the Problems) In order to achieve the above object, the present invention was 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 obtained by dissolving ground animal bone powder in sulfuric acid or hydrochloric acid, and an osteolytic solution obtained by dissolving calcined and powdered animal bone powder in sulfuric acid or hydrochloric acid, Alternatively, there is an animal bone-containing flocculant that is uniformly mixed with a metal solution dissolved in hydrochloric acid. In addition, 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 acid or hydrochloric acid, and then both solutions are mixed. A method for producing an animal bone-containing flocculant, characterized in that the animal bone-containing flocculant is made of 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 an osteolytic method in which calcined and powdered animal bone powder is dissolved in sulfuric acid or hydrochloric acid. An animal bone-containing flocculant, which is a uniform mixture of a liquid and a metal solution prepared by dissolving iron or copper in sulfuric acid or hydrochloric acid, is used after adding an alkaline reactive material to the treatment liquid. Methods for using animal bone-containing flocculants. In the above manufacturing method, calcined and powdered animal bone meal is mixed with sulfuric acid or hydrochloric acid at a ratio of about 1 to 1.5 of the latter to about 1 kg of the former to dissolve the bone powder,
After that, it is diluted with water and filtered to obtain a bone solution.Meanwhile, iron or copper and sulfuric acid or hydrochloric acid are mixed at a ratio of about 1 to 1.5 per about 100g of the former to dissolve the iron or copper, and then diluted with water. and filter to obtain a metal solution, and then combine the above bone solution and metal solution,
It is preferable to have a step of mixing and homogenizing the former at a volume ratio of about 0.3 to 0.7 to the latter. (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. (Example) (1) About the animal bone-containing flocculant The animal bones used as raw materials for the flocculant of the present invention are bones that have conventionally been mostly discarded at livestock farms, especially the 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 them melt during the boiling process during production, so they are not suitable for use as raw materials. The above-mentioned raw bones are cut into appropriate sizes and cut into sizes that are easy to burn, and then placed in a pressure cooker (compression cooker) at a temperature of about 90℃ at around 200-400℃.
Boil for a minute or so. Next, the bone is placed in a firing furnace and fired at around 900 to 1100°C for about 60 to 180 minutes, and then allowed to naturally cool in the furnace for around 60 minutes to return to room temperature or a state close to this temperature. Gelatin, fat, white matter,
If organic matter such as glue remains, it will cause oxidative decay, so it is important to ensure that it is removed. By the above-mentioned boiling process, most of the organic matter adhering not only to the outside but also inside the pores can be separated and removed from the bone. At this time, if the boiling is done at a lower temperature or for a shorter time than the above, the organic matter cannot be removed sufficiently, causing problems in the subsequent firing process. There is no advantage to using boiling conditions at a higher temperature or for a longer time than the above. In this way, by removing most of the organic matter in the boiling process and then passing through the baking process, the remaining organic matter can be completely removed, and at the same time, the humidity (moisture) in the bone can be reduced to preferably a few percent or less. can be reduced to almost 0%. Firing without a boiling step is not preferable because it causes significant combustion of organic matter and smoke generation, resulting in environmental pollution, discomfort during work, and damage to equipment. If the firing conditions are clearly lower than the above,
The bones will become carbonized, and if the temperature is too high, the bones will turn to ash, and in either case, the object will not function as intended by the present invention.
According to the above conditions, the bone becomes white and maintains its original state with numerous pores. After the above-mentioned firing and cooling, the bone is crushed and passed through a powder machine to obtain bone powder of approximately 20 to 200 meshes. In the case of bovine bones, the yield of the above-mentioned bone meal was approximately 40% by weight compared to raw raw bones. The particles are mainly composed of calcium, phosphorus, magnesium,
It is made of barium, sodium, sulfur, potassium, aluminum, iron, zinc, copper, nickel, etc., and has countless microscopic pores that communicate between the inside and outside of the particle. Ionization is alkaline due to calcium etc. The above bone powder and sulfuric acid are mixed at a ratio of about 1 to 1.5 of the latter to about 1 kg of the former, and the bone powder is dissolved over about 2 hours (or more), resulting in a mixture of about 8 to 12 times the ratio of the sulfuric acid. After diluting () with water, this is filtered to obtain osteolytic solution A. Note that hydrochloric acid may be used instead of sulfuric acid, but
When mixed with a metal solution to be described later, sulfuric acid is preferable in terms of its efficiency in dissolving iron or copper. The animal bone-containing flocculant of the present invention can be prepared by using only the above-mentioned osteolytic solution A. On the other hand, add iron or copper and sulfuric acid to 30 to 60 g of iron and 40 g of copper.
Mix the latter at a ratio of about 1 to 1.5 to ~70 g of the mixture, and dissolve the iron and copper over about 24 hours (or more), to a ratio of about 8 to 12 times the sulfuric acid ()
After diluting with water, this is filtered to obtain metal solution B. In addition, iron and copper are reactive with organic substances,
It has the function of further promoting coagulation and adding weight to aggregates to make them easier to settle. Copper is more effective, but for economical reasons it is better to mix it with iron. Next, the above-mentioned osteolysis solution A and metal solution B are mixed at a volume ratio of about 0.3 to 0.7 of the latter to 1 of the former, and in order to make the mixing uniform, the mixture is heated at 80 to 120°C, preferably around 100°C. Boil for around 30-60 minutes,
Thereafter, the animal bone-containing flocculant of the present invention can be obtained by filtration. 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. Therefore, when using this for wastewater, etc., it should be neutralized or alkalineized (7.0
~9.5, preferably 7.0 to 8.5), at the same time as the flocculant, an alkaline reactant such as caustic soda or nitric lime is mixed into the wastewater at a ratio of about 0.3 to 0.7 of the latter to 1 volume of the former. It is best to use it as If the wastewater has a high pH of 9.5 or higher, use an acidic reaction material such as dilute sulfuric acid. However, since domestic wastewater contains a considerable amount of salt, calcium, etc., the reaction can be sufficiently promoted without the addition of the above-mentioned reactants. (2) Regarding wastewater treatment using an animal bone-containing flocculant Next, an example of a method and an apparatus for treating wastewater using the animal bone-containing flocculant of the present invention will be explained based on the drawings. FIG. 1 is a flowchart of a treatment process suitable for treating wastewater from ordinary households, factories, and the like. The device has an animal bone-containing flocculant tank 1, a reactant (caustic soda, nitric lime, etc.) tank 2,
The wastewater is first injected into a measuring tank 3 for adjusting the amounts of the coagulant and reactant added, and then flows into the stirring tank 4 where the reactant and animal bone-containing coagulant are mixed in and thoroughly stirred by a stirrer. Then, the organic matter is flowed under pressure into the pressurized flotation tank 5 by a compressor to coagulate and float the organic matter. The stirring tank 4 may be divided into a flocculant mixing tank 4a equipped with a stirrer and a flocculation reaction tank 4b equipped with a stirrer. The treated water passes through a skimmer disposed at the upper part of the pressurized flotation tank 5 and flows into a 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 tank, where they are deposited as sludge. The filter tank 6 may be a layered layer of fine sand, which is made by kneading small pieces of animal bones calcined by the method of the present invention or pulverized animal bones and clay powder into granules. It may also be a stack of animal bone-containing granules that have been oxidized and fired. The former filtration layer can remove fine impurities after organic matter has been removed, so it can be used satisfactorily for general wastewater. 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. 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. 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. First, wastewater discharged directly from slaughterhouses, etc.
The water 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 passes through a measuring tank 12 that adjusts the flow rate and flow rate that can be processed per unit time, and then passes through a mixing tank 13.
It is introduced into the reaction tank 14. Both tanks are equipped with stirring blades, and are also connected with a reactant injection device 15 such as caustic soda or nitric lime, and an animal bone-containing flocculant injection device 16 according to the present invention, so that the pH of the wastewater can be adjusted. The reactant is injected to be within the range of 7.0 to 9.5, and a very small amount of animal bone-containing flocculant is added to the wastewater depending on the concentration of the wastewater (using the biochemical oxygen supply BOD as the measurement standard). Injected. For example, wastewater with a BOD of about 8001
Approximately 25 c.c. of animal bone-containing flocculant is injected into m 3 and mixed by stirring for approximately 1 to 5 minutes. The wastewater is then introduced into the pressurized flotation tank 17 from below under pressure by a compressor, and the aggregates that floated to the top due to the pressure are separated by a skimmer disposed above, and then Second reaction tank 1
It will be leaked on 8th. The aggregates floating upward and separated by the skimmer are discharged to the sludge thickening tank 31. The second reaction tank 18 is again injected with the required amount from the animal bone-containing flocculant injection device 19 and the reactant injection device 20 as necessary for pH adjustment, stirred and reacted, and then transferred to the coagulation sedimentation tank 21. The remaining organic matter that could not be completely separated in the pressurized flotation tank 17 is condensed and precipitated. The precipitate is discharged to the sludge thickening tank 31. After the treated water passes through a filter and is temporarily stored in a liquid storage tank 22, it is transferred to a vertically long filtration tank 23 in which sand is layered as a filter medium.
The liquid is transferred at a constant flow rate to flow down the filter tank 23 by gravity, and then stored in the liquid storage tank 24. 25 is animal bone obtained by kneading and granulating fine pieces of animal bone baked 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 baking clay as a binder into howder. This is a vertically long filtration tank made of layered main particles. 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 addition of ClO 2 from the sterilizer 26, is sterilized, and is stored in the treated water tank 27. Each of the filtration tanks 23 and 25 is for removing residual minute impurities, and the filtration tank 25 also has the function of alkaline ionizing the treated water using bone components such as calcium to turn it into mineral water. A backwashing blower 28 is connected to the treated water tank 27 via piping, and the treated water is forced to flow back into both the filtration tanks 23 and 25.If the treated water flows back into the filtration tank and is provided with a function for cleaning, the filtration tank can be cleaned. can be maintained over the long term without deteriorating 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. In addition, when the above-mentioned apparatus according to the present invention is combined with a wastewater treatment facility using a conventional activated sludge method or the like, 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 better to allow it to pass through a processing step. After the sludge accumulated in the sludge thickening tank 31 is concentrated, it is subjected to a sludge treatment process, excessively dried, and disposed of as appropriate, or it is subjected to a granulation process, then allowed to naturally ferment, and used as fertilizer or soil improvement material. can do. Since the sludge is a deposit of the organic matter, it exhibits excellent efficacy as a natural fertilizer or soil conditioner. Experimental example 1 Untreated wastewater (hereinafter referred to as raw water) A discharged from a meat center (slaughterhouse) located in Kumamoto Prefecture,
Treated water B in which the raw water was treated by a general activated sludge system installed in the company and currently in operation; and Treated water C in which the raw water was treated through the process according to the present invention shown in Figure 2. The results of the analysis at the Pharmaceutical Testing Center of the Kumamoto Prefectural Pharmacists Association were as shown in Table 1.

【表】【table】

【表】 BODは生物化学的酸素消費量、CODは化学的
酸素消費量、SSは懸濁物質である。分析方法は、
上記分析項目の上から順に規格12.1、環境庁告示
第59号、規格17、規格21、厚生省建設省令第1
号、環境庁告示第64号付表によつた。規格は
JISK0102である。 実験例 2 鹿児島県所在の或る食肉加工場(屠殺場)から
排出された原水A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に示すとおりであつた。
[Table] BOD is biochemical oxygen consumption, COD is chemical oxygen consumption, and SS is suspended solids. The analysis method is
From top to bottom, the above analysis items are Standard 12.1, Environment Agency Notification No. 59, Standard 17, Standard 21, and Ministry of Health, Labor and Welfare Construction Ordinance No. 1.
According to the attached table of Environment Agency Notification No. 64. The standard is
It is JISK0102. Experimental Example 2 Raw water A discharged from a meat processing plant (slaughterhouse) located in Kagoshima Prefecture and treated water C obtained by treating the raw water through the process according to the present invention shown in Fig. The results of the analysis by the Kagoshima Prefecture Pollution Control Association are as follows:
It was as shown in Table 2.

【表】 分析方法は実験例1と同じである。 実験例 3 北九州市所在の或る食肉センター(屠殺場)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装置装置によつて処
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に示すとおりであつた。
[Table] The analysis method was the same as in Experimental Example 1. Experimental Example 3 Raw water A discharged from a meat center (slaughterhouse) located in Kitakyushu City, and treated water B obtained by treating the raw water with a general activated sludge equipment installed at the company and currently in operation. The results of an analysis by the Kitakyushu City Environmental Improvement Association of the raw water and treated water C, which was processed through the process according to the present invention shown in Figure 2, are as follows.
The results were as shown in Table 3.

【表】 分析方法は、SSがJISK0102−14−1で、他は
実験例1と同じである。 実験例 4 福岡県所在の或る食肉加工場(屠殺場)から排
出された原水A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に示すとおりであつた。
[Table] The analysis method was the same as in Experimental Example 1 except that SS was JISK0102-14-1. Experimental Example 4 Raw water A discharged from a meat processing plant (slaughterhouse) located in Fukuoka Prefecture and treated water C obtained by treating the raw water through the process according to the present invention shown in Fig. The results of the analysis conducted by the Japan Environmental Health Center were as shown in Table 4.

【表】 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。 実験例 5 宮崎県所在の或るにわとり処理(ブロイラー)
会社から排出された原水Aと、該原水を会社に設
置され現運転中の一般的活性汚泥装置装置によつ
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、財団法人宮崎県公害防止協会で分析した結果
は、表5に示すとおりであつた。
[Table] The analysis method was the same as in Experimental Example 1 except that the coliform count was determined using the MPN method. Experimental example 5 A certain chicken processing (broiler) located in Miyazaki prefecture
Raw water A discharged from the company, treated water B obtained by treating the raw water with a general activated sludge equipment installed in the company and currently in operation, and the raw water according to the present invention shown in FIG. The results of an analysis of the treated water C that was processed through the process by the Miyazaki Prefecture Pollution Control Association were as shown in Table 5.

【表】【table】

【表】 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。未項目は環境庁告示第59号付
表7によつた。 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ーにより、
SSの処理は活性炭により行つていた。この水道
用取水に本発明に係る凝集剤を添加(取水1m3に
ついて20c.c.程度)したところ、有機物等の凝集が
顕著であり、各検査項目についての数値は、上記
従来の処理後の浄水に比して数10〜数100分の一
に減少し、特にCCDについての減少が著しかつ
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態でも明
確に表れた。 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しており、試料Bは弱腐敗臭
があつたが、試料Cはほとんど臭気が感じられな
かつた。また、試料Cは無色透明であつた。 試料Cは高い浄化力によつて飲料としてもよい
ほどに再生されており、これを20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。 以上から明らかなように、上記装置による再生
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、使用後の水を再び上記装置
によつて浄化すれば、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。 なお、上記処理によつ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。 (発明の効果) 以上のように、本発明によれば、従来決用法も
なく大方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、一次的濾過によつて
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つて、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
再生水を得るこたができ、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
単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。 動物骨溶解液だけの構成の凝集剤によれば、凝
集物を分離するためのフイ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、凝集物は凝固沈澱
するので、分離作業を容易にする。 本発明に係る凝集剤によつて浄化された再生水
は、広範囲での再利用に適している外、自然水域
に放流しても汚濁の危険性がない。 また、本発明によつ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つて浄化
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。
[Table] The analysis method is the same as in Experimental Example 1 for the top five analysis items above. Items not yet listed are based on Appendix Table 7 of Environment Agency Notification No. 59. Experimental example 6 Conventionally, tap water was disinfected using sodium hypochlorite, and BOD and COD were treated using sulfuric acid.
SS treatment was performed using activated carbon. When the flocculant according to the present invention was added to this tap water intake (approximately 20 c.c. per 1 m 3 of water intake), the flocculation of organic matter was remarkable, and the numerical values for each inspection item were as follows: The reduction was several 10 to several 100 times lower than that of purified water, and the reduction in CCD was particularly remarkable. When the flocculant according to the present invention was added to conventional water purification, the flocculation of organic substances was clearly visible even when visually observed. In addition, in any of the above experimental examples, sample A
sample B had a weak rotten odor, while sample C had almost no odor. Moreover, Sample C was colorless and transparent. Sample C has been regenerated to the point where it can be used as a drink due to its high purifying power, and 20 people tasted it and all found that it tasted similar to so-called natural mineral water, which is lighter and sweeter than tap water. I got it. As is clear from the above, when the recycled water produced by the above device is used as factory water or water for various purposes other than washing water, it can be used as recycled water any number of times if the water after use is purified again by the above device. This can help conserve water resources. In addition, the aggregates separated by the above treatment are
Since it is an organic substance, it can be used as fertilizer or compost with appropriate treatment. (Effects of the Invention) As described above, according to the present invention, an animal bone-containing flocculant can be produced by a simple method by utilizing animal bones, which have conventionally been discarded without any use. According to this flocculant, after removing relatively large solids through primary filtration, a sufficient condensation reaction is carried out to purify wastewater, especially wastewater containing putrefactive organic matter such as animal origin. At the same time, it is possible to obtain reclaimed water that has been mineralized and purified to a drinkable level, which can be processed in a relatively short period of time.In addition, the equipment for this purpose has a relatively simple structure and is inexpensive, and requires less maintenance. It can be made easily. If the flocculant is made up of only animal bone solution, it is necessary to use a filter to separate the aggregates, but if the flocculant is made up of a mixture of iron, copper, etc. metal solution, , the aggregates coagulate and precipitate, making the separation process easier. Reclaimed water purified by the flocculant according to the present invention is suitable for reuse over a wide range of areas, and there is no risk of pollution even when it is discharged into natural water bodies. Furthermore, when the recycled water obtained according to the present invention is used, if the water after use is purified again according to 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
の一例を示すフローチヤート図、第2図は同様廃
水処理の別の一例を示すフローチヤート図であ
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。
FIG. 1 is a flowchart showing an example of wastewater treatment using the flocculant according to the present invention, and FIG. 2 is a flowchart showing another example of the same wastewater treatment. 1,16...Animal bone-containing flocculant tank, 2,15...
...Neutralizer tank, 3, 12...Measuring tank, 4a, 13...
...Mixing tank, 4b, 14...Reaction tank, 5, 17...
Pressurized flotation tank, 6, 23, 25...filtration tank.

Claims (1)

【特許請求の範囲】 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。 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。 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。 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1〜1.5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に対して後者約1〜1.5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。 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。 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。
[Scope of Claims] 1. An animal bone-containing flocculant comprising an osteolytic solution prepared by dissolving calcined powdered animal bone powder in sulfuric acid or hydrochloric acid. 2. An animal bone-containing flocculant 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. 3. Mix calcined and powdered animal bone powder with sulfuric acid or hydrochloric acid to obtain a bone solution, and on the other hand, mix iron or copper with sulfuric acid or hydrochloric acid to obtain a metal solution, and then mix both solutions. A method for producing an animal bone-containing flocculant, which comprises mixing and integrating. 4 Mix calcined and powdered animal bone powder with sulfuric acid or hydrochloric acid at a ratio of about 1 to 1.5 of the latter to about 1 kg of the former to dissolve the bone powder, then dilute with water and filter to obtain a bone dissolution solution, On the other hand, iron to copper and sulfuric acid to hydrochloric acid are mixed in a ratio of about 1 to 1.5 of the latter to about 100 g of the former, the iron to copper is dissolved, and then diluted with water and filtered to obtain a metal solution. The above-mentioned osteolytic solution and metal dissolving solution are mixed to about 1 for the former and about 1 for the latter.
A method for producing an animal bone-containing flocculant comprising a step of mixing and homogenizing at a volume ratio of 0.3 to 0.7. 5 An animal bone characterized in that an animal bone-containing flocculant consisting of a bone dissolving solution prepared by dissolving calcined and 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 the included flocculant. 6. An animal bone-containing flocculant made 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. , A method for using an animal bone-containing flocculant, which comprises adding an alkaline reactive material to a treatment solution before use.
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
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
NZ22709388A NZ227093A (en) 1988-04-28 1988-11-25 Activating material comprising calcined bone; flocculating agents
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
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 JPH01274807A (en) 1989-11-02
JPH0553521B2 true 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)

Families Citing this family (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
AU2004220629A1 (en) * 2003-03-12 2004-09-23 3M Innovative Properties Company Polymer compositions with bioactive silver, copper or zinc compounds, medical articles, and processes
CN101346168B (en) * 2005-12-26 2012-05-23 艾克塞拉股份有限公司 coagulant
JP5770538B2 (en) * 2011-06-07 2015-08-26 堀邊 義一 Treatment method of 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
JP6837403B2 (en) * 2017-08-28 2021-03-03 水ing株式会社 Water treatment method for wastewater containing oil and water treatment equipment for wastewater containing oil

Also Published As

Publication number Publication date
JPH01274807A (en) 1989-11-02

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