JPH09299922A - Effective treatment of viscera of scallops - Google Patents

Effective treatment of viscera of scallops

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Publication number
JPH09299922A
JPH09299922A JP8160412A JP16041296A JPH09299922A JP H09299922 A JPH09299922 A JP H09299922A JP 8160412 A JP8160412 A JP 8160412A JP 16041296 A JP16041296 A JP 16041296A JP H09299922 A JPH09299922 A JP H09299922A
Authority
JP
Japan
Prior art keywords
protein
water
waste
filtrate
cadmium
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
JP8160412A
Other languages
Japanese (ja)
Inventor
Tomoji Tanaka
友爾 田中
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
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Filing date
Publication date
Application filed by Individual filed Critical Individual
Priority to JP8160412A priority Critical patent/JPH09299922A/en
Publication of JPH09299922A publication Critical patent/JPH09299922A/en
Pending legal-status Critical Current

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  • Meat, Egg Or Seafood Products (AREA)
  • Processing Of Solid Wastes (AREA)
  • Treatment Of Water By Ion Exchange (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
  • Water Treatment By Electricity Or Magnetism (AREA)
  • Water Treatment By Sorption (AREA)

Abstract

PROBLEM TO BE SOLVED: To execute a treatment in a short time by removing harmful materials from polluting processed marine product waste, etc., and eliminating the malodors and waste water contamination generated by an active sludge method treatment in the treatment of the waste. SOLUTION: The waste of cadmium-contg. contents and other marine and livestock processed products is boiled and separated. The waste formed by solidifying protein in such a manner is filtered out. Fats and oils and the protein are recovered from the waste. Further, the filtrate is treated with active carbon fermentation humic acid and protein flocculating material, by which the filtrate is filtered. Further, the filtrate is adsorbed by ion exchange resins. Adsorption media are added together with enzyme to the filtrate to adsorb the filtrate. The clean liquid is subjected to dephosphorization and denitrification by water hyacinth, etc., and thereafter, the liquid is released. The recovered protein is subjected to cadmium removal by an electrolytic acid alkaline liquid and alcohol water and is subjected to adsorption and purification by the ion exchange resins. The recovered cadmium filtrate is neutralized and is then washed with water. The protein is dried and the pulverized protein is used as animal feed and food or as a soil improving fertilizer. The washing liquid of the filtration is purified by the adsorption treatment with the ion exchange resins, etc., and is released.

Description

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

この発明は、従来焼却処理やコンクリート詰めされた公
害性水産加工廃棄物や畜産加工廃棄物から有害物を取り
去り、更に、これら廃棄物の処理に於いて実施されてい
た活性汚泥法処理が瀑気中に生ずる悪臭と排水汚染を改
善し、短時間処理法として煮沸する事によって蛋白質を
凝固し、水と蛋白質との分離を容易にすると共に、水に
溶けた蛋白質を凝固沈殿して水液中の凝固物を容易に瀘
別して悪臭の再発を防ぐと共に、瀘別した瀘液中のカド
ミウム重金属の公害物質をイオン交換樹脂や活性炭フミ
ン酸発酵材で凝集剤で処理して、吸着浄化した瀘別をラ
ヂエーション性カルシウム、ゼオライトのセラミックス
で吸着し、水草と分解酵素で分解した脱燐窒瀘別を放流
し、更に、煮沸凝固した蛋白質の瀘別した固形物は電解
隔膜で作った酸、アルカリ水と電解隔膜分離した瀘液を
中和して有害金属イオンをイオン交換樹脂と活性炭フミ
ン酸発酵物と硫酸鉄で処理して吸着除去し、更に瀘別し
た排水をカルシウムゼオライトセラミックスで吸着し、
水草で処理して脱燐窒して放流せしめる時は、B.O.
Dは公知の2分の1に減少し、又、処理時間も活性汚泥
法では12時間かかるものが約1時間以内の処理で行わ
れる利点があり、又、蛋白質や油脂の様に分解して悪臭
を生じやすい廃棄物の短時間処理と煮沸する殺菌法によ
る結果、二次悪臭が生じない利点があり、又、カツオの
血水の排水の場合でも加熱による蛋白質の凝固は蛋白血
液の分離を容易とし、含有するホルモンや分解酵素の悪
臭をも分離を容易にする為、従来の活性汚泥法に於ける
爆気による悪臭物の拡散は阻止されるから二次汚染は無
いし、海洋汚染や河川への放流による過剰燐酸、窒素化
合物の濃度規制が容易となり畜産加工に於ける血水の処
理にも有効に利用される。特に、ソーセージ加工に於け
る蛋白質のスラヂやスカムケーキを煮沸する時は、悪臭
の要因を阻止し、瀑気槽の必要もなく濃縮槽の設置の必
要もない。これは、蛋白質の加熱凝固による水との分離
が容易となり殺菌による蛋白質の加水分解が停止される
為に悪臭がなく、排水の透明度は10mに及ぶ良い結果
を得る。又、電解に於いては、隔膜電解を行う事によっ
て電解質として芒硝を使用する時は、陽極に硫酸液10
%前後の液が作られ、又、陰極には苛性アルカリ液が作
られ更に、この電解隔膜を以て中空室を作る時は、中性
液が得られると共にこの中に凝固した蛋白質のアルコー
ルアルカリ液を入れて電解するとカドミウムは陰極室内
に集中して分解精製が行われる。そして、陽極液で中和
するとPH値の調整が容易となる。又、この陽極に鉄極
で電解すると硫酸鉄の酸性液が出来、活性炭発酵フミン
液にこの硫酸鉄を入れて加温すると血水の様なものも凝
集沈殿し且つ、吸着されて悪臭は脱臭され澄明液が出来
るから排水の浄化が行われるが、この処理に於ける排水
中にもカドミウムや重金属有害物を除去するには、イオ
ン交換樹脂による浄化を行う時は、カドミウムの回収吸
着が行われ排水中のカドミウムの公害は殆どない。又、
ラヂエーションカルシウム、ゼオライト30%:70%
の割合で混合したものを焼成温度800℃で仮焼した素
燐棒やペレット球をタンク中に入れて、アスペルギリウ
ス菌、蛋白分解酵素、リパーゼを入れたタンクに排水を
浸漬せしめて吸着させたものは脱色も同時に行われるの
で澄明排水に変化し、水液中の可溶油脂分解物も除去さ
れるが、この排水中には燐酸液、硫酸液、窒素化合物液
が残留するからこれらは水草の毛根で吸収せしめて脱燐
窒を行う窒素化合物のアンモニアは硫酸と反応して硫安
となれば毛根が吸収されやすくなるから、この排水を放
流すればB.O.Dは1P.P.M程度の放流され公害
性は無い。この排水中の燐酸やアンモニア、食塩水、硫
酸塩の多い場合は前記隔膜電解の中室に入れて電解除去
すれば公害性は無い。この様に本願の処理方法は、常に
悪臭公害に悩まされる水産加工及び畜産加工物の処理に
於いて瀑気分解処理に長時間のかかる処理法を加熱クッ
カーで電気ボイラーで処理する時は、30〜60分で瀘
別まで行われ油脂の分離までも同時に行われるから悪臭
性は無いが、簡単な鉄錫で煮沸した内臓物は腐敗や蛋白
分解が行われる以前に直ちに処理する時は、悪臭は無く
なる利点があるが、公害のカドミウム等の有害物が蛋白
質とキレート化されたものは蛋白質との分離が容易では
なく、処理薬品の浸透性が悪いので凝固化せしめる時は
かえって分離が酸、アルカリ抽出する方法が容易であ
る。又、回収油脂は水添して化粧品、食品に利用され、
蛋白質は飼料、肥料に利用される為、その処理費用の5
0〜80%をまかなえる特徴があり、透明液は10mで
も見えるので今後の水処理法の改善ともなる。又、この
有害カドミウムの為に、特に帆立貝の内臓物は焼却処分
されていた処理費コストが煮沸に代用される時には燃費
は半減するので有利であり、産業上有用な発明である。
この発明の実施要領を図面で説明すると、次の如くであ
る。
This invention removes harmful substances from pollution-related marine product processing wastes and livestock processing wastes that have been conventionally incinerated or packed with concrete, and further, activated sludge method treatment that has been carried out in the treatment of these wastes is deficient. It improves the malodor and wastewater pollution that occur inside and coagulates the protein by boiling as a short-time treatment method, facilitating the separation of water and protein, and coagulating and precipitating the protein dissolved in water The coagulated product is easily filtered to prevent the reoccurrence of bad odors, and the cadmium heavy metal pollutants in the filtered filtrate are treated with a flocculant using an ion exchange resin or activated carbon humic acid fermenting material and adsorbed and purified. Is adsorbed by radiative calcium and zeolite ceramics, discharged dehydrogenation and nitrogen separation decomposed by aquatic plants and decomposing enzymes, and further, the solidified product obtained by separation of boiled and coagulated protein by an electrolytic membrane, Lucari water and the filtrate separated by the electrolytic membrane are neutralized, and harmful metal ions are adsorbed and removed by treatment with ion-exchange resin, activated carbon humic acid ferment and iron sulfate, and the filtered wastewater is adsorbed with calcium zeolite ceramics. ,
When it is treated with aquatic plants, dephosphorylated, and discharged, B. O.
D is reduced to one half of the known value, and the treatment time is 12 hours by the activated sludge method, but it has the advantage of being treated within about 1 hour, and it is decomposed like proteins and oils and fats. As a result of the short-time treatment of wastes that tend to give off a bad odor and the sterilization method of boiling, there is an advantage that a secondary bad odor does not occur, and even when bonito blood water is drained, protein coagulation by heating facilitates the separation of protein blood. Since the odors of contained hormones and degrading enzymes can be easily separated, the diffusion of odors due to the blast in the conventional activated sludge method is prevented, so there is no secondary pollution, and there is no marine pollution or river pollution. The concentration of excess phosphoric acid and nitrogen compounds can be easily regulated by the release to the river, and it can be effectively used for the treatment of blood water in livestock processing. In particular, when boiling protein sludge and scum cake in sausage processing, it prevents odorous factors, and it is not necessary to install a gas tank or a concentration tank. This is because the protein is easily separated from water by heating and coagulation and hydrolysis of the protein is stopped by sterilization, so that there is no bad odor, and the transparency of the drainage is as good as 10 m. In addition, in the electrolysis, when sodium sulfate is used as the electrolyte by performing diaphragm electrolysis, the sulfuric acid solution 10 is used as the anode.
%, A caustic alkali solution is made at the cathode, and when a hollow chamber is made with this electrolytic diaphragm, a neutral solution is obtained and the alcohol-alkaline solution of the protein coagulated therein is obtained. When placed and electrolyzed, cadmium concentrates in the cathode chamber for decomposition and purification. Then, neutralization with the anolyte facilitates adjustment of the PH value. Also, electrolysis of this anode with an iron electrode produces an acidic solution of iron sulfate, and when this iron sulfate is added to the activated carbon fermented humic acid solution and heated, things such as blood water also agglomerate and settle, and the bad odor is absorbed and deodorized. The effluent is purified because a clear liquid is produced.To remove cadmium and heavy metal harmful substances in the effluent during this treatment, the cadmium is recovered and adsorbed when the ion exchange resin is used for purification. There is almost no pollution of cadmium in the wastewater. or,
Radiation calcium, zeolite 30%: 70%
Mix the mixture in the proportion of calcination temperature of 800 ℃ and put the phosphorous rods and pellet spheres in the tank, and immerse the wastewater in the tank containing Aspergillus bacterium, proteolytic enzyme, and lipase for adsorption. Since it is also decolorized at the same time, it changes to clear wastewater and soluble oil and fat decomposition products in the water solution are also removed, but since phosphoric acid solution, sulfuric acid solution and nitrogen compound solution remain in this wastewater, these Ammonia, which is a nitrogen compound that is absorbed by the roots of aquatic plants and dephosphorylated, reacts with sulfuric acid to become ammonium sulfate, so that the roots are easily absorbed. O. D is 1P. P. It is released to the extent of M and has no pollution. If the wastewater contains a large amount of phosphoric acid, ammonia, saline, or sulfate, it is not harmful if it is electrolytically removed by placing it in the inner chamber of the diaphragm electrolysis. In this way, the treatment method of the present application is a treatment method that takes a long time for decomposing water vapor in the processing of fishery products and livestock products that are constantly suffering from bad odor pollution. It does not have a bad odor because it is separated in 60 minutes and the separation of fats and oils is done at the same time. However, the internal organs boiled with simple iron-tin are odorless when they are immediately processed before being decomposed or proteolytically decomposed. However, it is not easy to separate proteins from toxic substances such as cadmium, which is a pollutant, and proteins are chelated, and since the permeability of the treatment chemicals is poor, the separation is rather acid. The method of alkali extraction is easy. The recovered fats and oils are hydrogenated and used for cosmetics and foods.
Since protein is used for feed and fertilizer, its processing cost is 5
It has a feature of covering 0 to 80%, and since the transparent liquid can be seen even at 10 m, it will be an improvement in future water treatment methods. Further, because of the harmful cadmium, especially when the cost of the scallop's internal organs is incinerated and replaced by boiling, the fuel consumption is halved, which is an industrially useful invention.
The embodiment of the present invention will be described below with reference to the drawings.

【図1】は、水産加工、畜産加工を処理する工程図を示
し、先ず、養殖帆立貝を採集(4b)し貝殻(1a)と
帆立貝柱(1c)と内臓物(1b)とに分別(2a)し
て分離した貝殻(1a)は水洗し、脱水(3a)せしめ
たものを発酵分解(3’a)して粉砕(4a)して選別
(5a)を行い浄化剤(6a)として利用する。 この
内臓物(1bは、帆立貝柱(1c)を取り、区別して貝
柱(1c)は水洗して脱水(2c)を行ったものを冷凍
食品(3c)として冷凍保存し、包装して出荷する。内
臓物(1b)は、水で水洗したものを煮沸タンク(2
b)に投入し水蒸気90℃以上で加熱し、上澄液を汲み
取り油水分離器(3b)に掛けて油脂(4b)を分離し
瀘液(5b)を次の処理に廻すが、この内臓(1b)の
加熱凝固物は分離器に掛けて脱水(6b)して粉砕機
(7’b)に掛けて粉砕して脱カドミウム工程に入る。
これは、
FIG. 1 shows a process diagram for processing fishery processing and livestock processing. First, cultured scallops are collected (4b) and separated into shells (1a), scallops (1c) and offal (1b). ), The separated shell (1a) is washed with water, dehydrated (3a), fermented and decomposed (3'a), crushed (4a), sorted (5a) and used as a purifying agent (6a). . The offal (1b) is taken from the scallop scallop (1c), and the scallop (1c) is washed separately with water and dehydrated (2c), which is then frozen and stored as frozen food (3c) before being packaged and shipped. The internal organs (1b) are washed with water and boiled in a boiling tank (2
It is put in b) and heated with steam at 90 ° C. or higher, and the supernatant liquid is pumped up and applied to the oil-water separator (3b) to separate the oil and fat (4b), and the filtrate (5b) is sent to the next treatment. The heat-coagulated product of 1b) is placed in a separator, dehydrated (6b), and placed in a grinder (7'b) to be ground to enter a cadmium-free process.
this is,

【図2】の電解器のアルカリ液槽(4E)に蛋白質を浸
漬してカドミウムイオンを蛋白質(4E)かせ遊離せし
めたものを分離器(3E)で分離し、瀘液(3’E)と
アルカリ蛋白質(6E)に分離し、アルカリ蛋白質(6
E)は
[Fig. 2] The protein is immersed in the alkaline solution tank (4E) of the electrolyzer shown in Fig. 2 and cadmium ions are made to be protein (4E) to be liberated, and separated by a separator (3E) to obtain a filtrate (3'E). Separated into alkaline protein (6E),
E) is

【図4】k三室電解器で中性質(10F)に入れて電極
(4F)(4’F)で電解精製(7E)して脱アルカリ
を行う。このアルカリイオンとカドミウムイオンは陰極
室に移動し、中性室(10F)は中性となるから電解精
製が行われる。これによって分離されたアルカリ水とカ
ドミウム水は分離器で瀘別(9E)されて瀘液は中和剤
器(13E)で中和され、イオン交換樹脂(15E)で
処理されて脱カドミウムされた液(15’E)は吸着精
製タンクにポンプで送られ精製液に合流して使用する。
この時分離理された蛋白質(10E)は水洗処理(12
E)されて酸で中和(13E)されて水洗した蛋白質は
加熱タンク(17E)から真空乾燥機(18E)で処理
されて乾燥蛋白質(21E)を作る。 この時に出来る
水液(15’E)は発酵木材繊維(19E)と菌と共に
混合して含水80%として発酵室で発酵されて有機肥料
(20E)を作る。一方、乾燥蛋白質(21E)は、配
合飼料(22E)と30%混合して蛋白飼料を作る。こ
れには、カドミウムは無い。次に、瀘液(6b)は、活
性炭フミン酸を入れた吸着精製タナク(7b)で吸着と
脱色(7’b)が行われ水液を浄化した後、瀘過器(8
b)で処理され固形吸着剤(9b)と分離してこの固形
吸着剤は濾過後、400℃で加熱再生する。この瀘液
(10b)は、次の吸着精製タンク(11b)にポンプ
で導入してラヂエーション性カルシウムとゼオライトを
20:80の割合で混合した焼成棒(11’b)をいれ
たタンク(11b)で吸着を行い約10分後でその液を
濾過器(12b)で処理して、この瀘液精製液(13
b)はイオン交換器(14b)で脱カドミウムを行い脱
カドミウム液(15b)を作り、これを水(18b)と
混合して放流(17b)する。 この工程中に出る排水
は吸着精製タンク(11b)に送られて吸着浄化されて
順次浄化される。この時の排水中のカドミウムは、0.
001%以下で公害性は無い。又、脱蛋白質中のカドミ
ウムはの含有量は0.002%に低下する。この帆立貝
の廃棄物が他の水産加工物の廃棄物と混合された場合で
も同様に加熱せしめて蛋白質を凝固すれば、次後の工程
での悪臭は予防される。即ち、一般公知の瀑気槽による
酸化分解菌による分解法では常温分解である為、分解に
よる電気を吹き込んでもB.O.Dが1000P.P.
Mの汚水を分解するには12〜20時間を要し更に、ス
カムケキ量も一定以下に分解されない欠点がありその間
悪私有公害性があるが、煮沸法を採用すれば90℃で1
0〜15分で蛋白質は凝固し、悪臭要因の分解菌は消失
するから次後の悪臭発生は少ない。又、酸化脂肪の悪臭
は水添によって脱臭され飽和脂肪酸が得られる。各工程
で発生する水洗水は、活性炭フミン酸で処理されセラミ
ックスで吸着浄化されて、水草で更に脱燐脱窒されて無
公害性の排水を放出する事になり常に、B.O.Dは1
P.P.M程度で放流される。又、ソーセーヂ加工の汚
水処理は、動物蛋白質のスラヂが1〜3%に及ぶ場合が
あり、発酵分解すると有機酸の発生で悪臭は益々強烈と
なるから瀘別したスクリーニングによるスラヂも煮沸す
る事によって蛋白質が凝固すると悪臭は防止される。
又、カツオ加工の血水排水は煮沸によって血液は凝固す
るので、水と蛋白質の分離が容易となる。屠殺所の排水
に於いては、内臓物中にはホルモン、臓汁液、蛋白分解
酵素のペプシン、トリプシ、乳酸、吉草酸その他の悪臭
物や糞尿物が多量に混入しているから発酵フミン酸繊維
にアスペルギリウス菌とパパイア酵素を混合して、60
℃で発酵せしめた工程を導入すると悪臭は1:1の割合
で直ちに消失するから、汚水もこの繊維に吸着して発酵
熱80℃で発酵する時は、汚水は蒸発分解するので併用
すると良い。又、一般の活性汚泥法処理では瀑気槽に膨
大な面積を要するが、煮沸法では10分の1程度で充分
である。 水産加工工場に於ける汚水に於いてB.O.
Dは約4000P.P.Mであり、加工魚残骸は加工団
地で10ton/日に及ぶ事もあるから、煮沸法は資源
回収に役立つ特徴がある。
FIG. 4k is a three-chamber electrolyzer and put in a medium-quality (10F) electrolytically refined (7E) electrode (4F) (4′F) to carry out dealkalization. These alkali ions and cadmium ions move to the cathode chamber, and the neutral chamber (10F) becomes neutral, so that electrolytic refining is performed. The alkaline water and the cadmium water thus separated are separated (9E) by a separator, the filtrate is neutralized by a neutralizer (13E), treated with an ion exchange resin (15E), and decadmized. The liquid (15'E) is pumped to the adsorption purification tank and combined with the purification liquid for use.
At this time, the separated protein (10E) was washed with water (12
The protein E), neutralized with acid (13E) and washed with water, is processed with a vacuum dryer (18E) from a heating tank (17E) to make a dried protein (21E). The water liquid (15'E) formed at this time is mixed with the fermented wood fiber (19E) and the bacterium to be fermented in the fermentation chamber to have a water content of 80% to produce an organic fertilizer (20E). On the other hand, dried protein (21E) is mixed with the compounded feed (22E) at 30% to make a protein feed. It has no cadmium. Next, the filtration liquid (6b) is adsorbed and decolorized (7'b) by adsorption purification Tanac (7b) containing activated carbon humic acid to purify the water liquid, and then filtered (8
It is treated with b) and separated from the solid adsorbent (9b), and this solid adsorbent is filtered and regenerated by heating at 400 ° C. This filtrate (10b) was introduced into the next adsorption purification tank (11b) by a pump, and a firing rod (11'b) containing a mixture of radiative calcium and zeolite at a ratio of 20:80 was placed in the tank (11b). After about 10 minutes, the liquid was treated with a filter (12b) to obtain the filtered liquid (13).
In b), decadmium is removed by an ion exchanger (14b) to prepare a decadmium liquid (15b), which is mixed with water (18b) and discharged (17b). The wastewater discharged during this process is sent to the adsorption purification tank (11b) and is adsorbed and purified to be successively purified. The cadmium in the wastewater at this time was 0.
There is no pollution at 001% or less. Further, the content of cadmium in the deproteinized protein is reduced to 0.002%. Even when this scallop waste is mixed with the waste of other processed marine products, if it is heated in the same manner to coagulate the protein, the malodor in the subsequent steps is prevented. That is, since the decomposition method by the oxidative-decomposing bacteria in the publicly known waterfall tank is decomposition at room temperature, even if the electricity for the decomposition is blown, the B. O. D is 1000P. P.
It takes 12 to 20 hours to decompose the sewage of M, and there is a drawback that the amount of scum rake is not decomposed below a certain level. During that time, there is bad private pollution, but if the boiling method is adopted, it will be 1 at 90 ° C.
The protein coagulates in 0 to 15 minutes, and the degrading bacteria causing the malodorous substance disappears, so that the next generation of malodorous substance is small. Further, the malodor of the oxidized fat is deodorized by hydrogenation to obtain a saturated fatty acid. The rinsing water generated in each process is treated with activated carbon humic acid, adsorbed and purified with ceramics, and further dephosphorized and denitrified with aquatic plants to release pollution-free wastewater. O. D is 1
P. P. It is released at about M. In addition, the sewage treatment of sausage processing may cause the sludge of animal protein to reach 1 to 3%, and when fermented and decomposed, the foul odor becomes more and more intense due to the generation of organic acid. Therefore, the sludge obtained by the screening is also boiled. When the protein coagulates, the odor is prevented.
In addition, since blood is coagulated by boiling bonito-processed blood water drainage, separation of water and protein becomes easy. In slaughterhouse effluent, a large amount of hormones, viscera, proteolytic enzymes pepsin, trypsin, lactic acid, valeric acid, and other malodorous substances and manure are contained in the internal organs. Mix Aspergillus and papaya enzyme into
When the process of fermenting at ℃ is introduced, the malodor immediately disappears at a ratio of 1: 1. Therefore, when sewage is also adsorbed on this fiber and fermented at a fermentation heat of 80 ℃, sewage evaporates and decomposes, so it is recommended to use it together. Further, in the case of general activated sludge method treatment, a huge water tank requires a huge area, but in the boiling method, about 1/10 is sufficient. Sewage in a fish processing plant B. O.
D is about 4000P. P. Since it is M, and the processed fish debris can reach 10 ton / day in the processed complex, the boiling method has a feature of being useful for resource recovery.

【図2】は、電解液芒硝水(2F)を隔膜(3F)の電
解槽(1F)に入れた隔膜電解器の側面図を示すもの
で、陰極室(W)と陽極室(V)に入れた芒硝液は50
〜60ボルト0.1〜1アンペアーの電力を陽極(4
F)陰極(4’F)に印加する時は、陽極室液は酸性、
陰極室はアルカリ液の苛性液となるから、これら貯酸性
水槽(8F)とアルカリ水槽(8’F)に移行し、これ
を帆立貝内臓物の煮沸後の脱カドミウム浸漬液に使用
し、陽極の酸性水と硫酸鉄液は中和と凝集剤液として利
用する。この陽極や陰極室の両液の減少量はタンク(6
F)(6’F)から補給し、一定水準に併せて調整する
安価な方法では、繊維の毛管吸収作用を利用して行う。
この酸性液とアルカリ液は、前述に説明している。
FIG. 2 is a side view of a diaphragm electrolyzer in which an electrolyte solution, sodium mirabilite (2F), is placed in an electrolytic cell (1F) of a diaphragm (3F). The cathode chamber (W) and the anode chamber (V) are shown in FIG. 50 glauber's salt solution was added
~ 60 volts 0.1-1 ampere power (4
F) When applied to the cathode (4'F), the anolyte compartment liquid is acidic,
Since the cathode chamber becomes a caustic liquid of alkaline liquid, it is transferred to these acidic water storage tank (8F) and alkaline water tank (8'F), and this is used as a decadmium immersion liquid after boiling of scallop internal organs, Acidic water and iron sulfate solution are used as neutralizing and coagulant solution. The amount of reduction of both liquids in the anode and cathode chambers is
F) An inexpensive method of replenishing from (6′F) and adjusting to a certain level is performed by utilizing the capillary absorption effect of fibers.
The acidic liquid and the alkaline liquid have been described above.

【図3】は、隔膜電解槽の側面図を示し、陰極室(U)
のアルカリ電解水を入れ少量のアルコール液を入れて陽
極室にもアルカリ水液を入れて陽極室をアルカリ性とし
て電解する。その陽極室(W)と陰極室(U)とに篭を
入れて、その内部に煮沸した蛋白質の粉砕した顆粒物を
入れて電解すると、陽極室(W)内の篭の(9F)
(9’F)の内部蛋白質煮沸顆粒物は陽極室のアルカリ
液によりカドミウムイオンは隔膜を通じて陰極室に移動
し、陰極室のアルカリ液はアルカリイオンとカドミウム
イオンが増大して蛋白質から遊離する。これを脱水器に
掛けて瀘別し、脱水蛋白顆粒を回収し水洗したものを更
に、
FIG. 3 shows a side view of the diaphragm electrolyzer, showing the cathode chamber (U).
Alkaline electrolyzed water is added, a small amount of alcohol solution is added, and an alkaline water solution is also added to the anode chamber to make the anode chamber alkaline and electrolyze. A basket is placed in the anode chamber (W) and the cathode chamber (U), and crushed granules of boiled protein are put into the inside of the basket to electrolyze, and the basket in the anode chamber (W) (9F)
In the inner protein boiled granules of (9′F), cadmium ions move to the cathode chamber through the diaphragm by the alkaline liquid in the anode chamber, and the alkaline liquid in the cathode chamber is liberated from the protein by increasing the alkali ions and cadmium ions. This is put on a dehydrator and filtered, and the dehydrated protein granules are collected and washed with water.

【図4】の3室隔膜電解槽の中央室(10F)に篭(9
FF)内部嵌挿して中性水を電解液とし1〜3%の薄い
芒硝水を陽極室(W)と陰極室(U)に入れて、50ボ
ルト0.1アンペアーで電解すると、陽極室は酸性液と
なり陰極室はアルカリ液となり中室中の中性液は薄い酸
性芒硝液となるから、アルカリ水を添加して中性とする
と、含カドミウムイオンは陰極室に流されて遊離するか
ら、この液をイオン交換樹脂で吸着したカドミウムを回
収する。その時、中性液ないしアルカリ液の中央室
(Z)には、次第に蛋白質中のカドミウムは遊離し、そ
の濃度は次第に減少するので脱カドミウムに利用され
る。この脱カドミウムした蛋白質顆粒は篭(9FF)の
引揚げによって脱水され、これを水洗して脱水器で脱水
したものを真空加熱乾燥せしめて飼料原料と肥料原料に
利用する。この回収量は水産加工団地によって事なるが
鳥取の場合では500kg〜1200kg/月の脱カド
ミウム加工品が得られる。油脂は、300kg程度であ
る。この結果、煮沸に要するコストはこの一部の売上げ
でカバーされ、従来の活性汚法による方法とではかなり
のコスト低下となる。帆立貝のみの場合では、貝の浄化
剤への利用も考えられるが、雑水産加工工場の廃棄物と
同時に行えば飼料、肥料原料の使用量も量産化されるの
で経済性が高い。又、一般公知の活性汚泥法では、先ず
汚水をスクリーニングしてスラヂを除去したスラヂを産
廃物として処理する外、汚水の沈殿物のスカムケーキを
更に脱水瀘別して回収し、これも又産廃物として処理し
なければならない経費のかかる仕事であり、更に、湿気
槽による酸化分解中に生ずる悪臭ガスは予防が完全では
無いから大気汚染で問題となっている。従って、これら
を解決する為には煮沸法でないと解決出来ず、更に浄化
した活性汚泥法ではB.O.Dが20P.P.M以下が
制限範囲となっているが、血水の様な水の可溶のものの
浄化は困難であり、煮沸法と吸着脱色法の採用によって
解決でき、B.O.Dは1P.P.M以下に低下する。
この加熱も夜間電力を電気ボイラーとクッカー加熱缶の
使用によって無臭の状態で処理され、一連の処理工程は
60分以内で処理される。又、焼却炉の焼却処分の従来
法との皮革に於いては、カドミウムは灰中に一部を残留
し、他は揮発して大気汚染となるばかりでなく、灰の二
次処理を行う必要がある。本願の加熱を重油で行う時
は、1ton当り300kg/重油/日であるが、焼却
の場合は1ton当り2〜3tonの消費量である。こ
れは、含水量が85%〜90%の産廃物を焼却する為に
炉の補修が3ケ月に1度行う欠点がある。そして、資源
活用と公害性の問題は解決出来ず塩分による有毒塩素化
合物ガスの発生も解決せねばならない欠点がある。
FIG. 4 shows a basket (9) in the central chamber (10F) of the three-chamber diaphragm electrolyzer.
FF) Insert the solution into the anode chamber (W) and the cathode chamber (U) with neutral water as an electrolytic solution, and put 1 to 3% of thin sodium sulfate water into the anode chamber (U) and electrolyze at 50 volts and 0.1 amperes. Since it becomes an acidic liquid, the cathode chamber becomes an alkaline liquid, and the neutral liquid in the middle chamber becomes a thin acidic Glauber's salt solution, so when alkaline water is added to make it neutral, the cadmium-containing ion is released into the cathode chamber, Cadmium adsorbed on this liquid with an ion exchange resin is recovered. At that time, the cadmium in the protein is gradually released into the central chamber (Z) of the neutral solution or the alkaline solution, and the concentration thereof is gradually reduced, so that it is used for decadmium. The decadmium-depleted protein granules are dehydrated by withdrawing a basket (9FF), washed with water, dehydrated with a dehydrator, and dried under vacuum to be used as a feed material and a fertilizer material. The amount of recovery depends on the fish processing complex, but in the case of Tottori, 500 kg to 1200 kg / month of decadmium processed products can be obtained. Fats and oils are about 300 kg. As a result, the cost required for boiling is covered by a part of the sales, and the cost is considerably reduced as compared with the conventional method using the activated pollution method. If only scallops are used, it can be considered to be used as a purification agent for shellfish, but if it is carried out at the same time as the waste from the miscellaneous seafood processing plant, the amount of feed and fertilizer raw materials used will be mass-produced, which is highly economical. In addition, in the generally known activated sludge method, first, the sludge is screened to remove the sludge and the sludge is treated as industrial waste, and the scum cake of the sediment of the wastewater is further filtered by dewatering and collected. It is a costly task that must be treated and, in addition, the malodorous gases produced during oxidative decomposition in a moist tank are a problem with air pollution due to incomplete prevention. Therefore, in order to solve these problems, it can be solved only by the boiling method, and by the further purified activated sludge method, B. O. D is 20P. P. Although the range below M is the limit range, it is difficult to purify soluble substances such as blood water, which can be solved by adopting the boiling method and the adsorptive decolorization method. O. D is 1P. P. It falls below M.
This heating is also performed at night without electric power by using an electric boiler and a cooker heating can, and a series of treatment steps are performed within 60 minutes. Also, in the case of leather with the conventional method of incineration in an incinerator, cadmium not only partially remains in the ash and the other volatilizes to cause air pollution, and it is necessary to perform a secondary treatment of the ash. There is. When heavy oil is used for heating in the present application, the amount of consumption is 300 kg / ton of heavy oil / day, but in the case of incineration, the amount of consumption is 2-3 ton / ton. This has the drawback that the furnace is repaired once every three months in order to incinerate industrial waste with a water content of 85% to 90%. Further, there is a drawback that the problems of resource utilization and pollution cannot be solved, and the generation of toxic chlorine compound gas due to salt must be solved.

【図5】は、排水処理の工程図を示す。水産廃棄物を煮
沸して、油水分離気(2S)で油脂分を分離したものを
タンク(3S)に貯油し回収した後の排水をイオン交換
樹脂器(4S)で脱カドミウムを行い、酸アルカリで洗
滌して洗滌液を回収してカドミウムを回収する。次に、
イオン交換樹脂を通過した脱カドミウム排水は、ポンプ
(5S)でオートクレーブ(6S)に導入して、発酵繊
維フミン酸硫酸鉄活性炭(K)を篭(7S)に入れて加
温し70℃で吸着し、撹拌機(8S)で約30分間撹拌
しながら吸着した後、排水はオートクレーブ(9S)に
送り棒状に加工したラヂエーション炭酸カルシウム20
%ゼオライト80%を20%のポリビニールアルコール
水で素練りして棒滋養に押出機で押出した棒を乾燥して
個化せしめたものを800〜900℃で4時間〜10時
間加熱焼成した素練棒の吸着棒(OS)をオートクレー
ブ(9S)中に篏挿したオートクレーブ中に産廃を導入
して吸着処理し、上部に蛋白質分解酵素、その他の土壌
菌を入れて60℃吸着し分解を行わしめる。この上澄液
をパイプ(12S)で水耕槽(13S)に移行し、、ホ
テイ草(14S)で燐酸イオンとアンモニア、窒素化物
等を吸着せしめたものを、水と混合稀釈して排水する。
この排水のB.O.Dは1P.P.M以下となる。この
ホテイ草(14S)は、水面よりネットで回収しこれを
粉砕機(15S)で粉砕した後、混合機(16S)で発
酵槽(17S)(17’S)で樹皮、鋸屑、葉植物繊維
(18S)(18’S)をアスペルギリウス菌、茸菌を
ゼオライト粉に吸着した1g当りアスペルギリウス菌
(1億株吸着)を混合し、ホテイ草(14S)の粉砕物
を混合し、含水量80%として40〜60℃で発酵せし
めて分解した発酵フミン酸繊維(7S’)を60〜90
日静置発酵したものを吸着脱色処理のオートクレーブ
(6S)に活性炭(7’S)と共に篭内に入れて、排水
の浄化を行う。この活性炭はフミン酸を焼成温度500
℃〜600℃で加熱炭化し、更に1200℃で水蒸気を
吹き込み焼成して作る。又、回収油脂タンク(3S)か
らオートクレーブ(3’S)に送り30〜100kg圧
力で水素炭化でニッケル、コバルトの還元金属の触媒を
1〜3%混合して飽和油脂とする。この油脂が酸化され
た古い材料の場合は、苛性アルカリ水で精製して中和し
た油脂を作る。この排水処理に於ける活性炭50kg+
発酵フミン酸繊維50kgと自鉄鉱50gを袋に入れ
て、オートクレーブ(6S)に投入して吸着作用を行
う。この処理後の悪臭等は除去され、排水の透明度は1
mに及ぶが更にラヂエーシヨンカルシウム、ゼオライト
焼成棒による吸着による発酵酵素の作用によって分解し
1P.P.Mとなる。以上の様にこの発明の特徴は、従
来の多く実用化されている活性汚泥法が水産加工廃棄物
や畜産廃棄物処理に於いて廃棄物1tonに対し、約4
0tonの水を使用し瀑気を6時間〜10時間行う必要
があり、更に、温気後の上澄液をB.O.D5〜20
P.P.Mまで低下するには40〜60tonの水を要
し、その浄化液がB.O.D5〜20P.P.Mである
に対し、本発明の煮沸法は廃棄物1tonに対し2to
nの水の添加で充分である。これは、元々水溶性や加水
分解しやすい蛋白質を加熱により凝固せしめる事によっ
て20〜30分間の処理で澄明液となり蛋白質は沈殿す
るから、この澄明液から油脂を取り去り活性炭と発酵フ
ミン酸と少量の硫酸鉄、硫安、明バン、等で加温すると
水溶性の油脂と蛋白質は完全に沈殿吸着し、併せて脱臭
脱色が行われるそして透明度は、活性汚泥法に於いて今
尚黄色水となっているものがB.O.D5〜20P.
P.Mの場合、この活性炭発酵フミン酸、塩類の添加で
は無色に近いB.O.D1P.P.M以下に浄化され、
これを更にラヂエーシヨン性カルシウムゼオライト焼成
棒で酵素と共に吸着せしめる時は、可溶性のアミノ酸も
吸着除去される。そして、B.O.Dは0.5〜0.8
P.P.Mにまで低下し、加熱迅速処理により有害菌は
無く、完全な河川放流水となる。しかし、この浄化水中
にはアンモニア等の窒素化合物や燐酸塩が存在するので
これら水草に吸収すれば赤潮の要因を作らないばかりで
なく、水草は早期成長するからこの水草が二次公害とな
るので発酵繊維に混合してアスペルギリウス菌で分解せ
しめて発酵繊維を作る時は、発酵菌の増殖培養に役立
ち、発酵繊維のリサイクルができ肥料も廃棄蛋白質の発
酵と共に作られ又、吸着剤としての利用も可能となる。
特に、貝柱加工以外の水産物を処理する水産加工団地や
畜産加工工場に於いて、過剰の蛋白質廃棄物を処理する
時は、悪臭公害を予防するにも効果がある。そして、本
煮沸法によって出来た蛋白質廃棄物は瀘別して飼料に添
加して配合飼料を作り、鶏、牛、豚用に利用され、又、
養殖魚の飼料に利用されるから一般の活性汚泥法に於け
る汚泥物の様に、二次利用の殆ど出来ないスカムケーキ
の有効利用が可能となる。又、帆立貝の如く、カドミウ
ムの多い内臓物から脱カドミウムを行う事が出来るの
で、焼却処分していた内臓物の有効利用が可能となる。
又、市場やスーパー食品加工工場の廃棄物の処理に於い
ても、例えば、かさ高い野菜の処理に於いても煮沸法に
よってかさ高を防ぎ、発酵分解繊維との混合発酵によっ
て悪臭を予防し、公害性を少なくする。この悪臭ガス
は、発酵繊維を1:1の割合で処理すれば良い。又、カ
ドミウム処理に於いても、加熱処理する事によって粉砕
と抽出を容易にし且つ又、電解法によって精製する事は
カドミウム含有量を0.001%以下に低下する事が出
来、産業上有用な発明である。
FIG. 5 shows a process diagram of wastewater treatment. Boiled marine wastes are separated into oil and fat by oil-water separation air (2S) and stored in a tank (3S), and the wastewater after recovery is decadmized with an ion exchange resin vessel (4S) to obtain acid-alkali Wash with and collect the washing liquid to collect cadmium. next,
The decadmium wastewater that has passed through the ion exchange resin is introduced into an autoclave (6S) by a pump (5S), fermented fiber humic acid iron sulfate activated carbon (K) is placed in a basket (7S), heated and adsorbed at 70 ° C. Then, after adsorbing while stirring with a stirrer (8S) for about 30 minutes, the drainage was processed into an autoclave (9S) into a rod-shaped radiation calcium carbonate 20.
% Zeolite 80% was masticated with 20% polyvinyl alcohol water and extruded with an extruder to nourish the rod. The rod was dried and singulated, and heated and calcined at 800 to 900 ° C. for 4 hours to 10 hours. The adsorption rod (OS) of the kneading rod is inserted into the autoclave (9S) and the industrial waste is introduced into the autoclave for adsorption treatment, and proteolytic enzyme and other soil bacteria are put on the upper portion to adsorb at 60 ° C for decomposition. Close. This supernatant liquid is transferred to a hydroponic tank (13S) through a pipe (12S), and phosphate ions, ammonia, and nitrogen compounds adsorbed by Hotei grass (14S) are mixed with water, diluted and discharged. .
B. of this drainage O. D is 1P. P. It becomes M or less. This hot water grass (14S) is collected from the water surface with a net, crushed with a crusher (15S), and then fermenter (17S) (17'S) with a mixer (16S) to remove bark, sawdust, and leaf plant fibers. (18S) (18'S) is mixed with Aspergillus bacterium, and Aspergillus bacterium (100 million strains is adsorbed) per 1 g of the mushroom powder adsorbed on zeolite powder, and ground product of Hotei grass (14S) is mixed, Fermented humic acid fiber (7S ') decomposed by fermenting at 40-60 ° C with a water content of 80% is 60-90.
The fermented product that has been allowed to stand for a day is put into an autoclave (6S) for adsorptive decolorization together with activated carbon (7'S) in a basket to purify wastewater. This activated carbon burns humic acid at a temperature of 500
It is produced by heating and carbonizing at ℃ to 600 ℃, and then blowing steam at 1200 ℃ to burn. Further, the recovered oil / fat tank (3S) is sent to an autoclave (3 ′S) to mix 1 to 3% of a reduced metal catalyst of nickel and cobalt by hydrogen carbonization at a pressure of 30 to 100 kg to obtain a saturated oil and fat. If the fat is an old material that has been oxidized, it is refined with caustic water to neutralize it. Activated carbon 50kg + in this wastewater treatment
50 kg of fermented humic acid fibers and 50 g of iron ore are put in a bag and put into an autoclave (6S) to perform an adsorption action. After this treatment, odors etc. are removed and the effluent has a transparency of 1
However, it is decomposed by the action of a fermentation enzyme due to adsorption by a radiative calcium and a zeolite firing rod, and the amount of 1P. P. It becomes M. As described above, the feature of the present invention is that the activated sludge method, which has been widely put into practical use in the past, is about 4 to 1 ton of waste in processing of marine product processing waste and livestock waste.
It is necessary to use water of 0 ton for a period of 6 to 10 hours, and the supernatant after warming is added to B.I. O. D5-20
P. P. It takes 40 to 60 ton of water to decrease to M. O. D5-20P. P. In contrast to M, the boiling method of the present invention uses 2 tons for 1 ton of waste.
The addition of n water is sufficient. This is because the water-soluble and easily hydrolyzable protein is solidified by heating to form a clear solution in 20 to 30 minutes, and the protein precipitates. Therefore, oil and fat are removed from this clear solution and activated carbon, fermented humic acid and a small amount of it are removed. When heated with iron sulfate, ammonium sulfate, light vane, etc., water-soluble fats and oils are completely precipitated and adsorbed, and deodorization and decolorization are also performed.The transparency is still yellow water in the activated sludge method. What is present is B. O. D5-20P.
P. In the case of M, the addition of this activated carbon-fermented humic acid and salts made it almost colorless. O. D1P. P. Purified to below M,
When this is further adsorbed with the enzyme using a radiative calcium zeolite firing rod, soluble amino acids are also adsorbed and removed. And B. O. D is 0.5 to 0.8
P. P. It becomes as low as M, and there is no harmful bacterium due to the rapid heat treatment, and it becomes complete river discharge water. However, since nitrogen compounds such as ammonia and phosphates are present in this purified water, absorption by these aquatic plants not only causes a factor of red tide, but also because aquatic plants grow early, this aquatic plant becomes secondary pollution. When it is mixed with fermented fiber and decomposed with Aspergillus to make fermented fiber, it is useful for the growth culture of fermentative bacteria, the fermented fiber can be recycled, and the fertilizer is also produced with the fermentation of the waste protein. It can also be used.
In particular, when processing an excessive amount of protein waste in a fish processing complex or a livestock processing factory that processes marine products other than scallop processing, it is also effective in preventing foul odor pollution. Then, the protein waste produced by the main boiling method is filtered and added to the feed to make a compound feed, which is used for chicken, cow, pig, and
Since it is used as a feed for cultured fish, it is possible to effectively use the scum cake, which cannot be used for a secondary purpose like sludge in the general activated sludge method. Moreover, since cadmium can be removed from internal organs containing a large amount of cadmium, such as scallops, the internal organs that have been incinerated can be effectively used.
Also, in the treatment of waste in markets and super food processing plants, for example, in the treatment of bulky vegetables, bulkiness is prevented by the boiling method, and malodor is prevented by mixed fermentation with fermented fiber. Reduce pollution. With this malodorous gas, fermented fiber may be treated at a ratio of 1: 1. Also in the cadmium treatment, heat treatment facilitates crushing and extraction, and refining by the electrolytic method can reduce the cadmium content to 0.001% or less, which is industrially useful. It is an invention.

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

【図1】 帆立貝採集加工の工程図[Fig.1] Process drawing of scallop collecting

【図2】 酸アルカリ隔膜電解器の側面図FIG. 2 Side view of an acid-alkali membrane electrolyzer

【図3】 隔膜電解槽の側面図FIG. 3 Side view of diaphragm electrolyzer

【図4】 電解精製品の側面図[Figure 4] Side view of electrolyzed products

【図5】 煮沸法の工程図FIG. 5: Process diagram of boiling method

フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 C02F 3/32 C02F 3/32 // A23L 1/325 A23L 1/325 C Continuation of the front page (51) Int.Cl. 6 Identification code Office reference number FI Technical display location C02F 3/32 C02F 3/32 // A23L 1/325 A23L 1/325 C

Claims (1)

【特許請求の範囲】[Claims] 後文記載の如く、帆立貝の貝柱を採取した含カドミウム
内容物や他の水産、畜産加工廃棄物を、先ず、煮沸して
油脂を分離し、蛋白質を凝固せしめて次後の悪臭の発生
を防いだものを瀘別して、油脂、蛋白質を回収し、その
瀘液は活性炭発酵フミン酸と蛋白質凝集材で処理して瀘
別し、更に、その瀘液をイオン交換樹脂で吸着し、ラジ
エーシヨン性大理石とゼオライトを焼成した吸着媒で酵
素と共に添加して吸着し、浄澄液をホテイ草、水草等で
脱燐、脱窒せしめた後、放流せしめ回収蛋白質は、電解
酸アルカリ液とアルコール水で脱カドミウムを行い電解
精製せしめたイオン交換樹脂で吸着浄化して回収した脱
カドミウム瀘液を中和した後、水洗して精製し蛋白質は
真空乾燥機で乾燥して粉末化したものを動物飼料や、食
品として、又、土壌改良肥料として利用し、その瀘別水
洗液はイオン交換樹脂、活性炭フミン酸、カルシウム、
ゼオライトのセラミックス成型体、酵素、水草等で吸着
処理浄化して放流せしめる、水産加工廃棄物や畜産加工
廃棄物の加工利用する有効処理法。
As described later, the contents of cadmium containing scallop scallops and other marine and livestock processing wastes are first boiled to separate oils and fats, and the proteins are coagulated to prevent the subsequent generation of a bad odor. The oil and fat are recovered by separating the oil and protein, and the filtered solution is treated with activated carbon fermented humic acid and a protein coagulant to be filtered, and the filtered solution is adsorbed with an ion-exchange resin to produce a radiative marble. Zeolite is adsorbed by adding it with a calcined adsorbent together with an enzyme, and the purified solution is dephosphorized and denitrified with watery grass, aquatic plants, etc., and then discharged. Recovered protein is cadmium deoxidized with alkaline solution of electrolytic acid and alcohol water. After neutralizing the decadmium filtrate that has been adsorbed and purified with an electrolytically purified ion-exchange resin, it is washed with water and purified, and the protein is dried in a vacuum dryer and powdered into animal feed or food. As well as the soil Utilized as an improved fertilizer, its filtered off washing liquid ion exchange resins, activated carbon humic acid, calcium,
An effective treatment method for the processing and utilization of marine product processing waste and livestock processing waste, in which it is adsorbed by zeolite ceramics moldings, enzymes, aquatic plants, etc. and purified before being discharged.
JP8160412A 1996-05-18 1996-05-18 Effective treatment of viscera of scallops Pending JPH09299922A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP8160412A JPH09299922A (en) 1996-05-18 1996-05-18 Effective treatment of viscera of scallops

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP8160412A JPH09299922A (en) 1996-05-18 1996-05-18 Effective treatment of viscera of scallops

Publications (1)

Publication Number Publication Date
JPH09299922A true JPH09299922A (en) 1997-11-25

Family

ID=15714382

Family Applications (1)

Application Number Title Priority Date Filing Date
JP8160412A Pending JPH09299922A (en) 1996-05-18 1996-05-18 Effective treatment of viscera of scallops

Country Status (1)

Country Link
JP (1) JPH09299922A (en)

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002159952A (en) * 2000-11-28 2002-06-04 Japan Atom Energy Res Inst Method for removing harmful metal from waste viscus of scallop
JP2006158987A (en) * 2004-12-02 2006-06-22 Miyoshi Oil & Fat Co Ltd Method for removing heavy metal in marine product processing residue
JP2007229618A (en) * 2006-03-01 2007-09-13 Saga Univ Method for removing heavy metal from waste organ of scallop
WO2013031689A1 (en) * 2011-09-02 2013-03-07 東レ株式会社 Method and apparatus for purifying water containing radioactive substance and/or heavy metal
CN109772860A (en) * 2019-02-21 2019-05-21 环创(厦门)科技股份有限公司 The recycling treatment process of water hyacinth

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002159952A (en) * 2000-11-28 2002-06-04 Japan Atom Energy Res Inst Method for removing harmful metal from waste viscus of scallop
JP4547516B2 (en) * 2000-11-28 2010-09-22 独立行政法人 日本原子力研究開発機構 How to remove harmful metals from scallop scales
JP2006158987A (en) * 2004-12-02 2006-06-22 Miyoshi Oil & Fat Co Ltd Method for removing heavy metal in marine product processing residue
JP4632350B2 (en) * 2004-12-02 2011-02-16 ミヨシ油脂株式会社 Removal of heavy metals from fishery processing residue
JP2007229618A (en) * 2006-03-01 2007-09-13 Saga Univ Method for removing heavy metal from waste organ of scallop
JP4734643B2 (en) * 2006-03-01 2011-07-27 国立大学法人佐賀大学 Method for removing heavy metals from scallop visceral waste
WO2013031689A1 (en) * 2011-09-02 2013-03-07 東レ株式会社 Method and apparatus for purifying water containing radioactive substance and/or heavy metal
CN109772860A (en) * 2019-02-21 2019-05-21 环创(厦门)科技股份有限公司 The recycling treatment process of water hyacinth

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