JPH0427492A - Treatment of water - Google Patents
Treatment of waterInfo
- Publication number
- JPH0427492A JPH0427492A JP13105590A JP13105590A JPH0427492A JP H0427492 A JPH0427492 A JP H0427492A JP 13105590 A JP13105590 A JP 13105590A JP 13105590 A JP13105590 A JP 13105590A JP H0427492 A JPH0427492 A JP H0427492A
- Authority
- JP
- Japan
- Prior art keywords
- protein
- water
- flocculant
- salts
- blood
- 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
Links
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 16
- 235000018102 proteins Nutrition 0.000 claims abstract description 12
- 102000004169 proteins and genes Human genes 0.000 claims abstract description 12
- 108090000623 proteins and genes Proteins 0.000 claims abstract description 12
- 235000021120 animal protein Nutrition 0.000 claims abstract description 11
- 238000010438 heat treatment Methods 0.000 claims abstract description 11
- 239000008280 blood Substances 0.000 claims abstract description 10
- 210000004369 blood Anatomy 0.000 claims abstract description 10
- 238000001914 filtration Methods 0.000 claims abstract description 10
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims abstract description 9
- 229910052799 carbon Inorganic materials 0.000 claims abstract description 9
- 241000251468 Actinopterygii Species 0.000 claims abstract description 6
- 238000000034 method Methods 0.000 claims description 25
- 241001465754 Metazoa Species 0.000 claims description 5
- 150000001875 compounds Chemical class 0.000 claims description 3
- AZDRQVAHHNSJOQ-UHFFFAOYSA-N alumane Chemical class [AlH3] AZDRQVAHHNSJOQ-UHFFFAOYSA-N 0.000 claims description 2
- 159000000007 calcium salts Chemical class 0.000 claims description 2
- 159000000014 iron salts Chemical class 0.000 claims description 2
- 159000000003 magnesium salts Chemical class 0.000 claims description 2
- 150000003751 zinc Chemical class 0.000 claims description 2
- 239000002351 wastewater Substances 0.000 abstract description 19
- 239000002245 particle Substances 0.000 abstract description 3
- 244000144992 flock Species 0.000 abstract 2
- 150000003839 salts Chemical class 0.000 abstract 2
- 238000005345 coagulation Methods 0.000 description 6
- 230000015271 coagulation Effects 0.000 description 6
- TWRXJAOTZQYOKJ-UHFFFAOYSA-L Magnesium chloride Chemical compound [Mg+2].[Cl-].[Cl-] TWRXJAOTZQYOKJ-UHFFFAOYSA-L 0.000 description 4
- 239000000126 substance Substances 0.000 description 4
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 3
- 239000003513 alkali Substances 0.000 description 3
- 230000000052 comparative effect Effects 0.000 description 3
- 238000002474 experimental method Methods 0.000 description 3
- 238000000926 separation method Methods 0.000 description 3
- 239000000243 solution Substances 0.000 description 3
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 2
- 229910021578 Iron(III) chloride Inorganic materials 0.000 description 2
- 229910019142 PO4 Inorganic materials 0.000 description 2
- 239000002253 acid Substances 0.000 description 2
- 238000005119 centrifugation Methods 0.000 description 2
- 239000003795 chemical substances by application Substances 0.000 description 2
- 239000000701 coagulant Substances 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 239000008394 flocculating agent Substances 0.000 description 2
- RBTARNINKXHZNM-UHFFFAOYSA-K iron trichloride Chemical compound Cl[Fe](Cl)Cl RBTARNINKXHZNM-UHFFFAOYSA-K 0.000 description 2
- 229910001629 magnesium chloride Inorganic materials 0.000 description 2
- 239000005416 organic matter Substances 0.000 description 2
- 235000021317 phosphate Nutrition 0.000 description 2
- 150000003013 phosphoric acid derivatives Chemical class 0.000 description 2
- 229920001495 poly(sodium acrylate) polymer Polymers 0.000 description 2
- 238000001556 precipitation Methods 0.000 description 2
- 238000001223 reverse osmosis Methods 0.000 description 2
- NNMHYFLPFNGQFZ-UHFFFAOYSA-M sodium polyacrylate Chemical compound [Na+].[O-]C(=O)C=C NNMHYFLPFNGQFZ-UHFFFAOYSA-M 0.000 description 2
- 210000001179 synovial fluid Anatomy 0.000 description 2
- JIAARYAFYJHUJI-UHFFFAOYSA-L zinc dichloride Chemical compound [Cl-].[Cl-].[Zn+2] JIAARYAFYJHUJI-UHFFFAOYSA-L 0.000 description 2
- ATRRKUHOCOJYRX-UHFFFAOYSA-N Ammonium bicarbonate Chemical compound [NH4+].OC([O-])=O ATRRKUHOCOJYRX-UHFFFAOYSA-N 0.000 description 1
- 241000271566 Aves Species 0.000 description 1
- UXVMQQNJUSDDNG-UHFFFAOYSA-L Calcium chloride Chemical compound [Cl-].[Cl-].[Ca+2] UXVMQQNJUSDDNG-UHFFFAOYSA-L 0.000 description 1
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 description 1
- UEZVMMHDMIWARA-UHFFFAOYSA-N Metaphosphoric acid Chemical compound OP(=O)=O UEZVMMHDMIWARA-UHFFFAOYSA-N 0.000 description 1
- 229920002125 Sokalan® Polymers 0.000 description 1
- 150000008044 alkali metal hydroxides Chemical class 0.000 description 1
- 229910001860 alkaline earth metal hydroxide Inorganic materials 0.000 description 1
- DIZPMCHEQGEION-UHFFFAOYSA-H aluminium sulfate (anhydrous) Chemical compound [Al+3].[Al+3].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O DIZPMCHEQGEION-UHFFFAOYSA-H 0.000 description 1
- ANBBXQWFNXMHLD-UHFFFAOYSA-N aluminum;sodium;oxygen(2-) Chemical compound [O-2].[O-2].[Na+].[Al+3] ANBBXQWFNXMHLD-UHFFFAOYSA-N 0.000 description 1
- 150000001408 amides Chemical class 0.000 description 1
- 229910021529 ammonia Inorganic materials 0.000 description 1
- 239000001099 ammonium carbonate Substances 0.000 description 1
- 235000012501 ammonium carbonate Nutrition 0.000 description 1
- 238000009360 aquaculture Methods 0.000 description 1
- 244000144974 aquaculture Species 0.000 description 1
- 239000007864 aqueous solution Substances 0.000 description 1
- 238000009835 boiling Methods 0.000 description 1
- 235000008429 bread Nutrition 0.000 description 1
- 239000006172 buffering agent Substances 0.000 description 1
- 239000001110 calcium chloride Substances 0.000 description 1
- 229910001628 calcium chloride Inorganic materials 0.000 description 1
- 150000004649 carbonic acid derivatives Chemical class 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 230000001112 coagulating effect Effects 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 239000000645 desinfectant Substances 0.000 description 1
- 230000005611 electricity Effects 0.000 description 1
- 238000005868 electrolysis reaction Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 239000004744 fabric Substances 0.000 description 1
- 238000005188 flotation Methods 0.000 description 1
- 239000012530 fluid Substances 0.000 description 1
- 239000013505 freshwater Substances 0.000 description 1
- 150000002500 ions Chemical class 0.000 description 1
- FBAFATDZDUQKNH-UHFFFAOYSA-M iron chloride Chemical compound [Cl-].[Fe] FBAFATDZDUQKNH-UHFFFAOYSA-M 0.000 description 1
- 229910000358 iron sulfate Inorganic materials 0.000 description 1
- BAUYGSIQEAFULO-UHFFFAOYSA-L iron(2+) sulfate (anhydrous) Chemical compound [Fe+2].[O-]S([O-])(=O)=O BAUYGSIQEAFULO-UHFFFAOYSA-L 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 239000012528 membrane Substances 0.000 description 1
- 230000002175 menstrual effect Effects 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- TWNQGVIAIRXVLR-UHFFFAOYSA-N oxo(oxoalumanyloxy)alumane Chemical compound O=[Al]O[Al]=O TWNQGVIAIRXVLR-UHFFFAOYSA-N 0.000 description 1
- 238000010979 pH adjustment Methods 0.000 description 1
- 239000004584 polyacrylic acid Substances 0.000 description 1
- 239000002244 precipitate Substances 0.000 description 1
- 230000001376 precipitating effect Effects 0.000 description 1
- 230000004845 protein aggregation Effects 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
- 229910001388 sodium aluminate Inorganic materials 0.000 description 1
- 235000011121 sodium hydroxide Nutrition 0.000 description 1
- 238000003756 stirring Methods 0.000 description 1
- 239000011701 zinc Substances 0.000 description 1
- 239000011592 zinc chloride Substances 0.000 description 1
- 235000005074 zinc chloride Nutrition 0.000 description 1
Abstract
Description
【発明の詳細な説明】
〔産業上の利用分野〕
本発明は動物性血液等を含む高BOD排水の処理方法に
関する。DETAILED DESCRIPTION OF THE INVENTION [Industrial Field of Application] The present invention relates to a method for treating high BOD wastewater containing animal blood and the like.
魚類、獣類又は鳥類の解体時に排出される動物性血液を
含む排水の処理方法には次のような方法が知られている
。The following methods are known for treating wastewater containing animal blood discharged when fish, animals, or birds are butchered.
■加熱凝固tル過又は遠心分離法
■酸による凝固浜過又は遠心分離法
■凝集剤による凝固沈澱tル過又は遠心分離法■凝集剤
による凝固加圧浮上法
■蒸発缶による煮詰法
■電気分解法
■逆浸透法
加熱凝固法は、加熱凝固により除去できる蛋白質は原料
によって異なるが70〜80%であり、効果が少ない。■ Heating coagulation filtration or centrifugal separation method ■ Acid coagulation beach filtration or centrifugal separation method ■ Coagulation sedimentation using a coagulant filtration or centrifugation method ■ Coagulation pressurized flotation method using a coagulant ■ Boiling method using an evaporator ■ Electricity Decomposition method ■Reverse osmosis method Heat coagulation method is less effective, as the amount of protein that can be removed by heat coagulation varies depending on the raw material, but is only 70 to 80%.
酸による凝固沈澱法は回収蛋白質が利用し易い長所を持
っているが凝集剤を加える方法に比べて蛋白質の除去効
果が少なくこの方法だけでは排水基準内におさめるのは
難しい。凝集剤による沈澱法では、ポリアクリル酸ソー
ダ、ポリアクリル酸アミド、塩化第二鉄、メタリン酸等
による蛋白沈澱をtp過又は遠心分離する方法であるが
pHの調整を要する。凝固物には、沈澱するものと浮上
するものとがあり、浮上物には油を含む場合が多いので
、下から空気を吹込んで加圧し、凝固物を浮上させて除
去する。現在使用されている蛋白沈澱剤を加え適正なp
Hで処理しても、その除去率はBODとして50〜70
%である。The coagulation-precipitation method using acid has the advantage that the recovered protein can be easily used, but it is less effective in removing protein than the method of adding a flocculant, and it is difficult to keep the wastewater within the wastewater standards using this method alone. In the precipitation method using a flocculant, a protein precipitate using sodium polyacrylate, polyacrylic acid amide, ferric chloride, metaphosphoric acid, etc. is subjected to TP filtration or centrifugation, but pH adjustment is required. There are two types of coagulated substances: those that settle and those that float.The floating substances often contain oil, so air is blown from below and pressurized to float the coagulated substances and remove them. Add the currently used protein precipitants to ensure proper pH.
Even when treated with H, the removal rate is 50-70 as BOD.
%.
電気分解により排水中の蛋白質を凝固沈澱させる方法は
装置が安くつくが処理能力に問題がある。The method of coagulating and precipitating proteins in wastewater by electrolysis has inexpensive equipment, but has problems with processing capacity.
蒸発缶法は、排水を加熱蒸発し冷却凝集させて排出する
方法でCOD、BODの除去率は十分といえない。また
前処理として、できるだけ脂肪分を除いてお(必要があ
る。逆浸透法は水だけをとおし、イオン化物質をとおさ
ない半這膜を介して圧力により排水中の水のみを淡水の
方に押し出すものでBOD、CODの除去率は高いとさ
れているがある程度処理されて、有機物が少なくなった
ものでなければ実施が困難である。The evaporator method is a method in which wastewater is heated to evaporate, cooled and coagulated before being discharged, and the removal rate of COD and BOD cannot be said to be sufficient. In addition, as a pretreatment, it is necessary to remove as much fat as possible (reverse osmosis method allows only water to pass through, but only water in the wastewater is pushed out to fresh water by pressure through a semi-filtered membrane that does not allow ionized substances to pass through. It is said that the removal rate of BOD and COD is high, but it is difficult to implement unless the organic matter has been treated to some extent and the organic matter has been reduced.
本発明の目的は以上のような動物性蛋白質を含む排水の
全有機炭素分を減少させるのに適切な方法を提供するこ
とにある。An object of the present invention is to provide a method suitable for reducing the total organic carbon content of wastewater containing animal protein as described above.
本発明はすなわち動物性蛋白質を含む水に凝集剤として
鉄塩、アルミニウム塩、マグネシウム塩。In other words, the present invention uses iron salts, aluminum salts, and magnesium salts as flocculants in water containing animal protein.
カルシウム塩、亜鉛塩より選ばれた1種又は2種以上の
化合物を、上記蛋白質中の全有機炭素量の5〜200重
量%加え、pH3以上に調整し60℃以上に加熱後、凝
集物を炉別することを特徴とする水処理方法である。One or more compounds selected from calcium salts and zinc salts are added in an amount of 5 to 200% by weight based on the total amount of organic carbon in the protein, the pH is adjusted to 3 or higher, and after heating to 60°C or higher, the aggregates are removed. This is a water treatment method characterized by separating the water into different furnaces.
凝集剤として使用される化合物としては塩化鉄硫酸鉄、
硫酸アルミニウム、明パン、ポリ塩化アルミニウム、ア
ルミン酸ソーダ、塩化マグネシウム、塩化亜鉛、塩化カ
ルシウム等が挙げられ、これらの溶液を1種又は2種以
上組合せて使用することができる。またポリアクリル酸
ソーダ等の有機凝集剤を併用してもよい。凝集剤の添加
量は排水中に含まれる動物性蛋白質の全有機炭素量の5
〜200重量%、好ましくは40〜100重量%である
。次にアルカリ剤でpH3以上好ましくはp H6,5
〜7.5に調整する。アルカリ剤としてはアルカリ金属
の水酸化物、炭酸塩1重炭酸塩、アルカリ土類金属の水
酸化物、アンモニア、炭酸アンモニウム等が使用され緩
衝剤として第二燐酸アルカリ、第三燐酸アルカリ等を添
加することができる。加熱温度は60℃未満では蛋白質
の凝集が不完全であり最適温度は70〜80℃である。Compounds used as flocculants include iron chloride, iron sulfate,
Examples include aluminum sulfate, light bread, polyaluminum chloride, sodium aluminate, magnesium chloride, zinc chloride, calcium chloride, etc., and these solutions can be used alone or in combination of two or more. Further, an organic flocculant such as sodium polyacrylate may be used in combination. The amount of flocculant added is 5% of the total organic carbon content of animal protein contained in the wastewater.
-200% by weight, preferably 40-100% by weight. Next, use an alkaline agent to adjust the pH to 3 or higher, preferably pH 6.5.
Adjust to ~7.5. Alkali metal hydroxides, carbonates monobicarbonates, alkaline earth metal hydroxides, ammonia, ammonium carbonate, etc. are used as alkali agents, and dibasic alkali phosphates, tertiary alkali phosphates, etc. are added as buffering agents. can do. If the heating temperature is less than 60°C, protein aggregation will be incomplete, and the optimum temperature is 70 to 80°C.
凝集物のt戸別は通常の浜布等による沖過のほか遠心分
離等の方法によって行うことができる。The aggregates can be separated from house to house by a method such as centrifugal separation in addition to conventional filtration using Hama cloth or the like.
以下実施例、比較例により本発明方法の効果を説明する
。The effects of the method of the present invention will be explained below using Examples and Comparative Examples.
実施例1
養殖はまちの鮮血を含む排水(全有機炭素量TOC3,
300ppm)に凝集剤として塩化第二鉄、酸化アルミ
ニウム、塩化マグネシウムの水溶液(F e ’ 、
A I!3゛、 M g z +の全イオン濃度101
000ppを加え、苛性ソーダ溶液でpH6,5に調整
し、十分に攪拌後80℃に加熱し?p紙を使用してff
=過を行った。サンプル水100ccに対してt濾過時
間は1分間である。を月液は無色透明でありTOCは8
0ppmであった。Example 1 Aquaculture wastewater containing fresh blood from the town (total organic carbon content TOC3,
300 ppm) and an aqueous solution of ferric chloride, aluminum oxide, and magnesium chloride (F e ',
AI! 3゛, total ion concentration of M g z + 101
000pp was added, the pH was adjusted to 6.5 with a caustic soda solution, and after thorough stirring, the mixture was heated to 80°C. ff using p paper
= I made a mistake. The filtration time is 1 minute for 100 cc of sample water. The menstrual fluid is colorless and transparent and has a TOC of 8.
It was 0 ppm.
実施例2
実施例1の排水に同じ凝集剤の添加量を変えて同様の操
作で実験を行った。調整したpHは5.0〜7.0であ
り、加熱温度は80℃である。滑液のTOCは次表の如
くである。Example 2 An experiment was conducted in the same manner as in Example 1, except that the amount of the flocculant added was changed to the wastewater. The adjusted pH is 5.0 to 7.0, and the heating temperature is 80°C. The TOC of synovial fluid is as shown in the table below.
第1表
2 400 9B4
1.000 805
2.000 70
実施例3.比較例1
実施例1の排水に同じ凝集剤を200ppm添加し加熱
温度を変化させた以外は同様の操作で実験を行った。p
Hは8に調整し滑液のTOCは次表の如くである。Table 1 2 400 9B4
1.000 805
2.000 70
Example 3. Comparative Example 1 An experiment was conducted in the same manner as in Example 1, except that 200 ppm of the same flocculant was added to the wastewater and the heating temperature was changed. p
H was adjusted to 8, and the TOC of the synovial fluid was as shown in the following table.
(以下余白)
第2表
加熱温度60℃ではt月過速度が遅い。70℃以上では
清適速度は増加し100ccのサンプル液で2分である
。なお比較のため50℃で行ったがt濾過不能であった
。(Left below) Table 2 At a heating temperature of 60°C, the overspeed for t months is slow. At temperatures above 70°C, the cleaning speed increases to 2 minutes for 100 cc of sample liquid. For comparison, the test was carried out at 50°C, but filtration was not possible.
実施例4
実施例1の排水に添加する凝集剤の種類を変えて同様の
操作で実験を行った。pHは7.5、加熱温度は80℃
である。消液のTOCは次表の如くである。Example 4 An experiment was conducted in the same manner as in Example 1, except that the type of flocculant added to the wastewater was changed. pH is 7.5, heating temperature is 80℃
It is. The TOC of the disinfectant is as shown in the table below.
(以下余白)
第
表
F e Cj! 3
Fe”
ZnCj!z
Zn”
比較例2
実施例1の排水に凝集剤を加えず昇温しpH7にて浜過
を行ったところ供液のTOCは第4表のごとくであった
。(Left below) Table F e Cj! 3Fe" ZnCj!z Zn" Comparative Example 2 When the wastewater from Example 1 was heated without adding a flocculant and filtered at pH 7, the TOC of the solution was as shown in Table 4.
第4表
〔発明の効果〕
以上のように本発明方法によれば、動物蛋白質特に魚類
の鮮血を含む排水を凝集剤により加熱処理することによ
り、従来の加熱のみによる方法あるいは凝集剤のみによ
る方法に比べ凝集粒子がきわめて堀遇しやすい形態とな
り、蛋白質の除去率を向上させまたt%過速度を促進し
、排水の全有機炭素分をほぼ1soppm以下に減少さ
せることができるので工業的に有用である。Table 4 [Effects of the Invention] As described above, according to the method of the present invention, wastewater containing animal protein, particularly fresh fish blood, is heat-treated with a flocculant, thereby improving the effectiveness of the conventional heating-only method or the flocculant-only method. It is industrially useful because the aggregated particles become in a form that is extremely easy to excavate, improve the protein removal rate, promote t% overrate, and reduce the total organic carbon content of wastewater to approximately 1 soppm or less. It is.
Claims (3)
ミニウム塩、マグネシウム塩、カルシウム塩、亜鉛塩よ
り選ばれた1種又は2種以上の化合物を上記動物性蛋白
質中の全有機炭素量の5〜200重量%加え、pH3以
上に調整し60℃以上に加熱後、凝集物を濾別すること
を特徴とする水処理方法。(1) One or more compounds selected from iron salts, aluminum salts, magnesium salts, calcium salts, and zinc salts are added as a flocculant to water containing animal protein.Total organic carbon content in the animal protein A water treatment method characterized by adding 5 to 200% by weight of water, adjusting the pH to 3 or more, heating to 60° C. or more, and then filtering out aggregates.
白質である請求項1に記載の水処理方法。(2) The water treatment method according to claim 1, wherein the animal protein is a protein in fish blood or a fish body containing fish blood.
血液を含む動物体内の蛋白質である請求項1に記載の水
処理方法。(3) The water treatment method according to claim 1, wherein the animal protein is a protein in animal blood or bird blood or in an animal body containing these blood.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP13105590A JPH0427492A (en) | 1990-05-21 | 1990-05-21 | Treatment of water |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP13105590A JPH0427492A (en) | 1990-05-21 | 1990-05-21 | Treatment of water |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH0427492A true JPH0427492A (en) | 1992-01-30 |
Family
ID=15048958
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP13105590A Pending JPH0427492A (en) | 1990-05-21 | 1990-05-21 | Treatment of water |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH0427492A (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2002512123A (en) * | 1998-04-20 | 2002-04-23 | カルゴン コーポレイション | Inorganic composition, production method and method of use |
JP2003524524A (en) * | 2000-03-01 | 2003-08-19 | パーデュー・リサーチ・ファウンデーション | Organic wastewater treatment method in food processing plant |
Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS4878768A (en) * | 1972-01-24 | 1973-10-22 | ||
JPS541260A (en) * | 1977-06-04 | 1979-01-08 | Kawasaki Heavy Ind Ltd | Axial position adjusting apparatus for roll of rolling mills |
-
1990
- 1990-05-21 JP JP13105590A patent/JPH0427492A/en active Pending
Patent Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS4878768A (en) * | 1972-01-24 | 1973-10-22 | ||
JPS541260A (en) * | 1977-06-04 | 1979-01-08 | Kawasaki Heavy Ind Ltd | Axial position adjusting apparatus for roll of rolling mills |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2002512123A (en) * | 1998-04-20 | 2002-04-23 | カルゴン コーポレイション | Inorganic composition, production method and method of use |
JP2003524524A (en) * | 2000-03-01 | 2003-08-19 | パーデュー・リサーチ・ファウンデーション | Organic wastewater treatment method in food processing plant |
JP4688126B2 (en) * | 2000-03-01 | 2011-05-25 | パーデュー・リサーチ・ファウンデーション | Organic waste liquid treatment method in food processing factory |
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