JPH0229396B2 - - Google Patents
Info
- Publication number
- JPH0229396B2 JPH0229396B2 JP26255484A JP26255484A JPH0229396B2 JP H0229396 B2 JPH0229396 B2 JP H0229396B2 JP 26255484 A JP26255484 A JP 26255484A JP 26255484 A JP26255484 A JP 26255484A JP H0229396 B2 JPH0229396 B2 JP H0229396B2
- Authority
- JP
- Japan
- Prior art keywords
- hydrazine
- activated carbon
- containing water
- belt
- contact
- 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
Links
- OAKJQQAXSVQMHS-UHFFFAOYSA-N Hydrazine Chemical compound NN OAKJQQAXSVQMHS-UHFFFAOYSA-N 0.000 claims description 115
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims description 96
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 41
- 238000000034 method Methods 0.000 claims description 20
- 239000000835 fiber Substances 0.000 claims description 16
- 238000001179 sorption measurement Methods 0.000 claims description 8
- 239000000843 powder Substances 0.000 claims description 6
- 239000008187 granular material Substances 0.000 claims description 3
- 230000008929 regeneration Effects 0.000 claims description 2
- 238000011069 regeneration method Methods 0.000 claims description 2
- 239000000463 material Substances 0.000 claims 1
- 238000000354 decomposition reaction Methods 0.000 description 13
- 239000005708 Sodium hypochlorite Substances 0.000 description 7
- SUKJFIGYRHOWBL-UHFFFAOYSA-N sodium hypochlorite Chemical compound [Na+].Cl[O-] SUKJFIGYRHOWBL-UHFFFAOYSA-N 0.000 description 7
- 238000006243 chemical reaction Methods 0.000 description 5
- 238000005273 aeration Methods 0.000 description 4
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 4
- 239000001301 oxygen Substances 0.000 description 4
- 229910052760 oxygen Inorganic materials 0.000 description 4
- 238000005192 partition Methods 0.000 description 4
- 239000000126 substance Substances 0.000 description 4
- 229910001385 heavy metal Inorganic materials 0.000 description 3
- 239000002351 wastewater Substances 0.000 description 3
- 239000003054 catalyst Substances 0.000 description 2
- 239000000460 chlorine Substances 0.000 description 2
- 238000002347 injection Methods 0.000 description 2
- 239000007924 injection Substances 0.000 description 2
- 150000002505 iron Chemical class 0.000 description 2
- 238000006864 oxidative decomposition reaction Methods 0.000 description 2
- 238000012545 processing Methods 0.000 description 2
- 229920000049 Carbon (fiber) Polymers 0.000 description 1
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 1
- 239000000969 carrier Substances 0.000 description 1
- 229910052801 chlorine Inorganic materials 0.000 description 1
- 238000005345 coagulation Methods 0.000 description 1
- 230000015271 coagulation Effects 0.000 description 1
- 230000000052 comparative effect Effects 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 229910000365 copper sulfate Inorganic materials 0.000 description 1
- ARUVKPQLZAKDPS-UHFFFAOYSA-L copper(II) sulfate Chemical compound [Cu+2].[O-][S+2]([O-])([O-])[O-] ARUVKPQLZAKDPS-UHFFFAOYSA-L 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 238000011049 filling Methods 0.000 description 1
- 239000007789 gas Substances 0.000 description 1
- 150000002429 hydrazines Chemical class 0.000 description 1
- 238000005342 ion exchange Methods 0.000 description 1
- JEIPFZHSYJVQDO-UHFFFAOYSA-N iron(III) oxide Inorganic materials O=[Fe]O[Fe]=O JEIPFZHSYJVQDO-UHFFFAOYSA-N 0.000 description 1
- 239000007788 liquid Substances 0.000 description 1
- 238000012423 maintenance Methods 0.000 description 1
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical class C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 239000007800 oxidant agent Substances 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- JTJMJGYZQZDUJJ-UHFFFAOYSA-N phencyclidine Chemical compound C1CCCCN1C1(C=2C=CC=CC=2)CCCCC1 JTJMJGYZQZDUJJ-UHFFFAOYSA-N 0.000 description 1
- 230000003449 preventive effect Effects 0.000 description 1
- 239000002760 rocket fuel Substances 0.000 description 1
- 238000009287 sand filtration Methods 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
- 239000000243 solution Substances 0.000 description 1
- 238000003756 stirring Methods 0.000 description 1
- 238000012360 testing method Methods 0.000 description 1
- 238000010977 unit operation Methods 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/02—Aerobic processes
- C02F3/08—Aerobic processes using moving contact bodies
- C02F3/082—Rotating biological contactors
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/725—Treatment of water, waste water, or sewage by oxidation by catalytic oxidation
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Chemical & Material Sciences (AREA)
- Water Supply & Treatment (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Organic Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Health & Medical Sciences (AREA)
- Molecular Biology (AREA)
- Biodiversity & Conservation Biology (AREA)
- Microbiology (AREA)
- Removal Of Specific Substances (AREA)
- Water Treatment By Sorption (AREA)
Description
(産業上の利用分野)
本発明はヒドラジンを含有する水からヒドラジ
ンを除去する方法に関するものである。
(従来技術)
ヒドラジンは強い還元力を有しており、ボイラ
ー給水脱酸素剤、防錆剤、ロケツト燃料等の面で
輻広く使用されているが、ヒドラジンを含有した
水はヒドラジンがCOD成分であるため、そのま
まの形態では放流することができず、何らかの処
理を必要としている。処理方法としては種々の方
法があるが、今火力発電所排水の場合を例にとり
説明する。
火力発電所ではボイラー停止時にヒドラジンを
数十〜数百mg/添加して保罐することがよく行
われている。このヒドラジンを含有する水はボイ
ラ再起動時に数百〜数千m3非定常排水として排出
される。この排水のヒドラジンを除去する従来技
術として次亜塩素酸ソーダ等の酸化剤を添加し
酸化分解する方法および重金属等を触媒として
添加しエアレーシヨン酸化する方法がよく行われ
ている。
の方法については、例えば次亜塩素酸ソーダ
による酸化分解を例にとると、ヒドラジンと次亜
塩素酸ソーダとの反応は(1)式で示されるように当
量反応であるためヒドラジンはほぼ100%分解す
る。
N2H4+2NaOCl→2NaCl+N2+2H2O (1)
しかし、ヒドラジン1mg/ as N2H4に対し
次亜塩素酸ソーダを4.4mg/ as Cl2と多量に
添加しなければならずコストが高くなること、ま
たヒドラジン分解に要する次亜塩素酸ソーダ量の
コントロールは反応液の酸化還元電位を検出して
行うが、PHの影響を受けやすい等の理由で次亜塩
素酸ソーダを当量注入するのがなかなか難しい等
の問題点がある。次亜塩素酸ソーダの注入を残留
塩素計でコントロールする方法が提案されている
が(例えば土屋彦治「火力発電所のヒドラジン廃
水処理」PPM、1978/6g p21)、注入方式は
非常に複雑なものとなつている。
の方法は重金属(例えば硫酸銅)を触媒とし
て添加しエアレーシヨンによつてヒドラジンを酸
化する方法であり、反応式は(2)式で示される。
N2H4+O2→N2+2H2O (2)
この反応はPHの影響を大きく受け、アルカリ域
のほどヒドラジン分解速度は早い。しかし、添加
した重金属は有害であるため放流にあたつては除
去しておかねばならない。そのため凝集沈澱、砂
濾過、イオン交換等の単位操作が必要であり、そ
れに要する薬品代も無視し得ぬ金額となつてい
る。
またの方法の変法として活性炭または活性炭
と鉄塩とを添加してエアレーシヨンする方法が知
られている(特開昭54−23071)。しかし、この方
法も固液分離操作が前提となつており、特に粉末
活性炭を使用した場合は鉄塩等を凝集剤として添
加することが不可欠である。
このように従来のヒドラジン含有水の処理技術
は種々の問題点を有し改善すべき点が多い。
なお本出願に関連する技術としては、本出願と
同一の出願人による特願昭59−229292がある。
(発明が解決しようとする問題点)
本発明が解決しようとする問題点、すなわち、
目的は次の特徴を有するヒドラジン含有水の処理
方法を提供することである。
高価な薬品を使用しない
簡素で維持管理が容易
連続処理が可能
(問題点を解決するための手段)
本発明は活性炭とヒドラジン含有水を接触させ
ヒドラジンを活性炭へ吸着させる工程とヒドラジ
ンを吸着して吸着能力の低下した活性炭を強制的
に外気と接触させることにより吸着能力を回復さ
せる再生工程より構成されているが、活性炭とヒ
ドラジン含有水および空気との接触が一定時間毎
に交互に連続的に行えるよう工夫したものであ
る。すなわち活性炭を含む回転体またはベルトを
回転させ、一部がヒドラジン含有水と接触し、残
部が空気と接触するようにしたものである。
ここで、活性炭を含む回転体の形状は円板、円
柱状が好ましく、活性炭を円板または円柱状に成
形したもの、活性炭を円板または円柱状の支持体
に装着したもの、活性炭を円板状または円柱状の
支持体の内部に充填したものを1種または2種以
上の組合せで使用できる。
また、活性炭を含むベルトとは、活性炭をベル
ト状に成形したもの、ベルト状の支持体に装着お
よび(または)担持させたもの、ベルト状の支持
体の内部に充填したものを1種または2種以上の
組合せで使用できる。
使用する活性炭の形状は、粒状、粉末状、粉末
状のものを担体に担持したもの、繊維状、繊維を
布状にしたもの、繊維をハニカム状にしたもの、
繊維フエルト状にしたものなど種々の形状のもの
が使用できるが、粉末状のものはそのままでは取
扱いが面倒なので、なるべく担体に担持させたも
のがよい。
以上のような活性炭を含む回転体またはベルト
を回転させ、一部がヒドラジン含有水と残部が空
気と接触するようにすれば、活性炭とヒドラジン
含有水が接触している部分でヒドラジンの吸着と
一部分解が起こり、空気と接触している部分でヒ
ドラジンの分解と活性炭表面への酸素吸着が起こ
る。活性炭に吸着したヒドラジンは水中の溶存酸
素により一部分解するが、本発明では活性炭を強
制的に外気と接触させるので、活性炭表面と酸素
の接触面積が飛躍的に上昇し、吸着したヒドラジ
ンは短時間に分解してしまう。
活性炭を含む回転体の回転はモーターなどを使
用して行つてもよいが、ヒドラジン含有水中に空
気を導入し、曝気による撹拌力を動力として用い
てもよい。
かくして、本発明によれば何ら特殊な薬品を使
用せずともヒドラジンの吸着と分解を連続して行
うことができ、連続処理が可能となるのである。
(作用)
活性炭を円板に装着して使用する場合について
一実施態様を第1図に、また活性炭を円柱状の支
持体に充填して使用する場合について一実施態様
を第2図に示す。
第1図を参照しつつさらに詳細に説明する。
ヒドラジン含有水は原水流入管3よりヒドラジ
ン分解槽1に流入し、処理水流出管4より排出さ
れる。ヒドラジン分解槽1には多数の回転円板2
が回転軸5に取付けてあり、円板の下方部分がヒ
ドラジン含有水に浸りながら回転している。回転
円板2は円板状の支持体に活性炭素繊維を布状に
したもの、繊維をハニカム状にしたもの、粉末状
のものを担持したものなどを装着したものが使用
できる。ヒドラジン含有水は活性炭を装着した多
数の円板と接触し、ヒドラジンの吸着と分解を順
次繰返し、最終的にヒドラジン濃度の極めて低い
処理水となつて排出される。
第2図は、活性炭を円板状の支持体の内部に充
填したものであつて、活性炭の形状は粒状、繊維
状、繊維を布状にしたもの、繊維をハニカム状に
したもの、粉末状のものを粒状およびまたは布状
の担体に担持したものなどが使用できる。ただ
し、充填した活性炭が流出しないよう円柱状の活
性炭の外側をサランネツト、金網等で覆う必要が
ある。
活性炭をベルト状の支持体に装着して使用する
場合について一実施態様を第3図および第4図に
示す。
ヒドラジン含有水は原水流入管3よりヒドラジ
ン分解槽1に流入し、処理水流出管4より排出さ
れる。ヒドラジン分解槽1には、活性炭を装着し
たベルトが下方部分でヒドラジン含有水と接触し
ながら、2ケの回転軸によつて駆動している。活
性炭を装着するベルトとしては、どのようなもの
でもよいが、装着の容易な布状またはネツト状の
ものがよい。また活性炭の形状は粒状、粉末状も
使用できるが、繊維状、繊維をフエルト状にした
もの、繊維をハニカム状にしたものが装着しやす
い。これ等活性炭を2本のベルトにサンドイツチ
にして使用することもできる。
活性炭を装着したベルトが回転することによつ
てヒドラジンの吸着と分解が連続して起り、連続
処理が可能である。
第3図はベルトの回転軸が水平方向に取付けて
ある例であるが、第4図は垂直方向に取付け、さ
らにヒドラジン分解槽を仕切り板8によつて多数
の槽に分割し、各槽にベルトを取付けた例であ
る。
この例は、設置面積を少くし、ヒドラジンの除
去率を高めるのに有効である。
実施例 1
内径10cmの塩ビ管を2cmの幅で切断し、外側を
20メツシユの金網を覆い、内部に粒状活性炭(ツ
ルミコールGL−30商品名)を充填したもの5個
を、4cm毎に仕切りのある角型槽(幅12cm、長20
cm、高6cm)に第2図に示すような状態で設置し
た。この円柱5個を連結した回転軸を10rpmで回
転させ、槽の一端よりヒドラジン220mg/ as
N2H4含む合成原水を1/1hで通水し、処理水
を他端より排出した。なお、円柱の下方半分が水
中に浸漬するようにした。このようにして処理水
中のヒドラジン濃度を測定したところ、第1表の
とおりであつた。
(Industrial Application Field) The present invention relates to a method for removing hydrazine from water containing hydrazine. (Prior art) Hydrazine has strong reducing power and is widely used as a boiler feed water deoxidizer, rust preventive, rocket fuel, etc., but water containing hydrazine is a COD component. Therefore, it cannot be released as is and requires some kind of treatment. There are various treatment methods, but we will explain this using wastewater from a thermal power plant as an example. At thermal power plants, it is common practice to add tens to hundreds of milligrams of hydrazine to preserve the boiler when the boiler is shut down. This hydrazine-containing water is discharged as several hundred to several thousand m3 of unsteady wastewater when the boiler is restarted. Conventional techniques for removing hydrazine from this wastewater include a method in which an oxidizing agent such as sodium hypochlorite is added to perform oxidative decomposition, and a method in which a heavy metal or the like is added as a catalyst to perform aeration oxidation. Regarding the method, for example, if we take oxidative decomposition using sodium hypochlorite as an example, the reaction between hydrazine and sodium hypochlorite is an equivalent reaction as shown in equation (1), so hydrazine is almost 100% Disassemble. N 2 H 4 +2NaOCl→2NaCl+N 2 +2H 2 O (1) However, a large amount of sodium hypochlorite (4.4 mg/as Cl 2 ) must be added to 1 mg/as N 2 H 4 of hydrazine, resulting in high cost. The amount of sodium hypochlorite required for hydrazine decomposition is controlled by detecting the redox potential of the reaction solution, but it is difficult to inject an equivalent amount of sodium hypochlorite because it is easily affected by pH. There are some problems, such as it being quite difficult. A method has been proposed in which the injection of sodium hypochlorite is controlled using a residual chlorine meter (for example, Hikoji Tsuchiya, "Hydrazine Wastewater Treatment at Thermal Power Plants" PPM, 1978/6g p21), but the injection method is extremely complicated. It is becoming. The method is a method in which a heavy metal (for example, copper sulfate) is added as a catalyst and hydrazine is oxidized by aeration, and the reaction formula is shown by equation (2). N 2 H 4 +O 2 →N 2 +2H 2 O (2) This reaction is greatly affected by pH, and the more alkaline the region, the faster the hydrazine decomposition rate. However, the added heavy metals are harmful and must be removed before discharge. Therefore, unit operations such as coagulation sedimentation, sand filtration, and ion exchange are required, and the cost of chemicals required for these operations is also considerable. As a modification of the above method, a method is known in which activated carbon or activated carbon and iron salt are added for aeration (Japanese Patent Laid-Open No. 54-23071). However, this method also presupposes a solid-liquid separation operation, and especially when powdered activated carbon is used, it is essential to add iron salt or the like as a flocculant. As described above, the conventional treatment technology for hydrazine-containing water has various problems and there are many points to be improved. As a technology related to the present application, there is Japanese Patent Application No. 59-229292 filed by the same applicant as the present application. (Problems to be solved by the invention) Problems to be solved by the invention, namely:
The object is to provide a method for treating hydrazine-containing water having the following characteristics. Does not use expensive chemicals Simple and easy to maintain Continuous processing is possible (means to solve the problem) The present invention involves a process of bringing activated carbon and hydrazine-containing water into contact and adsorbing hydrazine to activated carbon. It consists of a regeneration process in which activated carbon whose adsorption capacity has decreased is forcibly brought into contact with outside air to restore its adsorption capacity. It has been devised so that it can be done. That is, a rotating body or belt containing activated carbon is rotated so that a part of the rotating body or belt comes into contact with hydrazine-containing water and the rest comes into contact with air. Here, the shape of the rotating body containing activated carbon is preferably a disc or a cylinder, and activated carbon is formed into a disc or cylinder, activated carbon is mounted on a disc or cylinder support, and activated carbon is formed into a disc or cylinder. One type or a combination of two or more types can be used by filling the inside of a cylindrical or cylindrical support. Furthermore, a belt containing activated carbon refers to activated carbon formed into a belt shape, attached to and/or carried on a belt-like support, or filled inside a belt-like support. Can be used in combinations of more than one species. The activated carbon used can be in the form of granules, powder, powder supported on a carrier, fibers, cloth-like fibers, honeycomb-like fibers,
It can be used in various shapes, such as in the form of fiber felt, but it is difficult to handle the powder as it is, so it is preferable to have it supported on a carrier. If a rotating body or belt containing activated carbon as described above is rotated so that a part of it comes into contact with hydrazine-containing water and the rest with air, hydrazine will be adsorbed and part of it will be absorbed in the part where activated carbon and hydrazine-containing water are in contact. The decomposition of hydrazine and the adsorption of oxygen on the surface of activated carbon occur in the area that is in contact with air. Hydrazine adsorbed on activated carbon is partially decomposed by dissolved oxygen in water, but in the present invention, the activated carbon is forced into contact with the outside air, so the contact area between the activated carbon surface and oxygen increases dramatically, and the adsorbed hydrazine is decomposed for a short time. It breaks down into The rotating body containing activated carbon may be rotated using a motor or the like, but air may be introduced into the hydrazine-containing water and the stirring force generated by aeration may be used as the motive power. Thus, according to the present invention, adsorption and decomposition of hydrazine can be carried out continuously without using any special chemicals, making continuous treatment possible. (Function) FIG. 1 shows an embodiment in which activated carbon is used by being attached to a disc, and FIG. 2 shows an embodiment in which activated carbon is used by being filled in a cylindrical support. This will be explained in more detail with reference to FIG. Hydrazine-containing water flows into the hydrazine decomposition tank 1 through a raw water inflow pipe 3 and is discharged through a treated water outflow pipe 4. The hydrazine decomposition tank 1 has many rotating disks 2.
is attached to a rotating shaft 5, and the lower part of the disc rotates while being immersed in hydrazine-containing water. The rotating disk 2 may be a disk-shaped support with cloth-like activated carbon fibers, honeycomb-like fibers, or powdered fibers supported on a disk-shaped support. The hydrazine-containing water comes into contact with a large number of discs equipped with activated carbon, and hydrazine is adsorbed and decomposed in sequence, and finally treated water with an extremely low hydrazine concentration is discharged. Figure 2 shows activated carbon filled inside a disc-shaped support, and the activated carbon can be in the form of granules, fibers, cloth-like fibers, honeycomb-like fibers, or powder. It is possible to use granular and/or cloth-like carriers. However, it is necessary to cover the outside of the cylindrical activated carbon with a saran net, wire mesh, etc. to prevent the filled activated carbon from flowing out. One embodiment of the case in which activated carbon is attached to a belt-like support is shown in FIGS. 3 and 4. Hydrazine-containing water flows into the hydrazine decomposition tank 1 through a raw water inflow pipe 3 and is discharged through a treated water outflow pipe 4. In the hydrazine decomposition tank 1, a belt equipped with activated carbon is driven by two rotating shafts while its lower part contacts the hydrazine-containing water. The belt on which the activated carbon is attached may be of any type, but a cloth-like or net-like one that is easy to wear is preferable. Activated carbon can be used in granular or powdered forms, but fibers, felt-like fibers, and honeycomb-like fibers are easier to attach. These activated carbons can also be used as sandwiched between two belts. By rotating the belt equipped with activated carbon, adsorption and decomposition of hydrazine occur continuously, making continuous processing possible. Figure 3 shows an example in which the rotation axis of the belt is installed in the horizontal direction, but in Figure 4, it is installed in the vertical direction, and furthermore, the hydrazine decomposition tank is divided into a number of tanks by a partition plate 8, and each tank is This is an example with a belt attached. This example is effective in reducing the footprint and increasing the removal rate of hydrazine. Example 1 A PVC pipe with an inner diameter of 10 cm was cut into 2 cm width, and the outside was
Five pieces of granular activated carbon (Tsurumicol GL-30 trade name) covered with a wire mesh of 20 mesh were placed in a square tank (width 12 cm, length 20 cm) with partitions every 4 cm.
cm, height 6 cm) as shown in Figure 2. The rotating shaft connecting these five cylinders was rotated at 10 rpm, and 220 mg/as of hydrazine was released from one end of the tank.
Synthetic raw water containing N 2 H 4 was passed through for 1/1 hour, and the treated water was discharged from the other end. Note that the lower half of the cylinder was immersed in water. When the hydrazine concentration in the treated water was measured in this way, the results were as shown in Table 1.
【表】
実施例 2
幅10cm、長さ40cmのサランネツトの両端をつな
ぎ、ベルト状にしたものの外周にフエルト状活性
炭素繊維(単繊維直径17μ、目付200g/m2)を
装着したものを、第3図に示すように、角型槽
(幅12cm、長20cm、高5cm)に設置し、ベルトの
速度が5cm/secとなるよう回転軸を回転させた。
槽の一端より各種濃度のヒドラジンを含む合成原
水を500ml/hの流量で流入させ、処理水を他端
より排出した。なお、槽の水位は2cmで、ベルト
の下半分が常に水中に浸漬している状態であつ
た。このようにして、処理水中のヒドラジン濃度
を測定したところ第2表のとおりであつた。[Table] Example 2 A saran net with a width of 10 cm and a length of 40 cm was connected at both ends to form a belt, and a felt-like activated carbon fiber (single fiber diameter 17 μm, basis weight 200 g/m 2 ) was attached to the outer periphery. As shown in Figure 3, it was installed in a square tank (width 12 cm, length 20 cm, height 5 cm), and the rotating shaft was rotated so that the belt speed was 5 cm/sec.
Synthetic raw water containing various concentrations of hydrazine was flowed into the tank from one end at a flow rate of 500 ml/h, and the treated water was discharged from the other end. The water level in the tank was 2 cm, and the lower half of the belt was always immersed in water. When the hydrazine concentration in the treated water was measured in this way, the results were as shown in Table 2.
【表】
比較例
実施例1に示す装置全体を密閉容器で覆い、
N2ガスを封入し、空気中の酸素を通常(21%)
の半分程度8〜12%および2〜5%にした場合に
ついて、実施例1の条件と同じ条件で試験した。
結果を第3表に示す。[Table] Comparative example The entire device shown in Example 1 was covered with an airtight container,
Filled with N2 gas, oxygen in the air is normally (21%)
Tests were conducted under the same conditions as in Example 1 for cases where the amount was reduced to approximately half of 8 to 12% and 2 to 5%.
The results are shown in Table 3.
【表】【table】
【表】
(発明の効果)
以上述べたように、本発明によればヒドラジン
の吸着と分解を何ら特殊な薬品を使用せず連続的
に行うことができる。したがつて、コストが低減
するばかりでなく、維持管理も容易となり、現場
作業者の安全衛生面でも寄与するところ大であ
る。[Table] (Effects of the Invention) As described above, according to the present invention, adsorption and decomposition of hydrazine can be carried out continuously without using any special chemicals. Therefore, not only costs are reduced, but maintenance and management are also facilitated, greatly contributing to the safety and health of field workers.
第1図は本発明の活性炭を円板に装着して使用
する場合の一実施態様を示す。第2図は本発明の
活性炭を円柱状の支持体の内部に充填して使用す
る場合の一実施態様を示す。第3図は本発明の活
性炭をベルトに装着したものを使用する場合の一
実施態様で第3図ではベルトの回転軸が水平方向
に取り付けてある例を示す。第4図は第3図の回
転軸が垂直方向に取付けてあり、さらに分解槽が
仕切り板によつて多数に分割されている場合の態
様を示す。
1……ヒドラジン分解槽、2……活性炭を装着
した円板、3……原水流入管、4……処理水排出
管、5,5′……回転軸、6……活性炭を充填し
た回転体、7……活性炭を装着したベルト、8…
…仕切り板。
FIG. 1 shows an embodiment in which the activated carbon of the present invention is mounted on a disk. FIG. 2 shows an embodiment in which the activated carbon of the present invention is used by being filled inside a cylindrical support. FIG. 3 shows an embodiment in which the activated carbon of the present invention is attached to a belt, and FIG. 3 shows an example in which the rotating shaft of the belt is attached in a horizontal direction. FIG. 4 shows an embodiment in which the rotating shaft shown in FIG. 3 is installed vertically, and the decomposition tank is divided into a large number of parts by partition plates. 1... Hydrazine decomposition tank, 2... Disc equipped with activated carbon, 3... Raw water inflow pipe, 4... Treated water discharge pipe, 5, 5'... Rotating shaft, 6... Rotating body filled with activated carbon , 7... Belt equipped with activated carbon, 8...
...Partition board.
Claims (1)
ジンを活性炭に吸着させる吸着工程およびヒドラ
ジンを吸着して吸着能力の低下した活性炭を水切
りした後、空気と接触させる再生工程よりなるヒ
ドラジン含有水の処理方法において、活性炭とヒ
ドラジン含有水および空気との接触を一定時間毎
に交互に行いながら、連続処理することを特徴と
するヒドラジン含有水の処理方法。 2 前記活性炭を円板または円柱状に成形したも
の、円板または円柱状の支持体に装着したもの、
円板または円柱状の支持体の内部に充填したもの
より選ばれた1種または2種以上のものを回転軸
に取付け、回転させるとともに回転している円板
または円柱の一部をヒドラジン含有水と接触さ
せ、他の部分を空気と接触するようにした特許請
求の範囲第1項記載のヒドラジン含有水の処理方
法。 3 前記活性炭をベルト状に成形したもの、ベル
ト状の支持体に装着したもの、ベルト状の支持体
の内部に充填したものより選ばれた1種または2
種以上を回転軸に取付け、ベルトを駆動させると
ともに、ベルトの一端をヒドラジン含有水と接触
させ、他端を空気と接触させるようにした特許請
求の範囲第1項記載のヒドラジン含有水の処理方
法。 4 前記活性炭の形状は粒状、粉末状、粉末状の
ものを担体に担持させたもの、繊維状、繊維をフ
エルト状にしたもの、繊維をハニカム状にしたも
のより選ばれた1種または2種以上よりなる特許
請求の範囲第1項、第2項または第3項のヒドラ
ジン含有水の処理方法。[Scope of Claims] 1. A hydrazine-containing method comprising an adsorption step in which activated carbon and hydrazine-containing water are brought into contact and hydrazine is adsorbed onto the activated carbon, and a regeneration step in which the activated carbon, which has adsorbed hydrazine and has a reduced adsorption capacity, is drained and then brought into contact with air. 1. A method for treating hydrazine-containing water, characterized in that the treatment is carried out continuously while bringing activated carbon into contact with hydrazine-containing water and air alternately at regular intervals. 2 The activated carbon formed into a disc or cylinder, or mounted on a disc or cylinder support;
One or more selected materials filled inside a disk or columnar support are attached to a rotating shaft, and as the disk or column is rotated, a part of the rotating disk or column is filled with hydrazine-containing water. The method for treating hydrazine-containing water according to claim 1, wherein the other portion is brought into contact with air. 3 One or two selected from the activated carbon formed into a belt shape, attached to a belt-shaped support, and filled inside a belt-shaped support.
A method for treating hydrazine-containing water according to claim 1, which comprises: attaching a seed or more to a rotating shaft, driving a belt, and bringing one end of the belt into contact with the hydrazine-containing water and the other end with air. . 4. The shape of the activated carbon is one or two selected from granules, powder, powder supported on a carrier, fibers, felt fibers, and honeycomb fibers. A method for treating hydrazine-containing water according to claim 1, 2, or 3, comprising the above.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP59262554A JPS61141988A (en) | 1984-12-12 | 1984-12-12 | Treatment of water containing hydrazine |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP59262554A JPS61141988A (en) | 1984-12-12 | 1984-12-12 | Treatment of water containing hydrazine |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS61141988A JPS61141988A (en) | 1986-06-28 |
| JPH0229396B2 true JPH0229396B2 (en) | 1990-06-29 |
Family
ID=17377415
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP59262554A Granted JPS61141988A (en) | 1984-12-12 | 1984-12-12 | Treatment of water containing hydrazine |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS61141988A (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US7758757B2 (en) * | 2007-10-19 | 2010-07-20 | E. I. Du Pont De Nemours And Company | Method for removing hydrazine compounds |
| GB201516253D0 (en) * | 2015-09-14 | 2015-10-28 | Univ Montfort | Rotating contactor reactor |
-
1984
- 1984-12-12 JP JP59262554A patent/JPS61141988A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS61141988A (en) | 1986-06-28 |
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