JPH0440055B2 - - Google Patents
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- Publication number
- JPH0440055B2 JPH0440055B2 JP58160673A JP16067383A JPH0440055B2 JP H0440055 B2 JPH0440055 B2 JP H0440055B2 JP 58160673 A JP58160673 A JP 58160673A JP 16067383 A JP16067383 A JP 16067383A JP H0440055 B2 JPH0440055 B2 JP H0440055B2
- Authority
- JP
- Japan
- Prior art keywords
- phosphoric acid
- exhaust gas
- odor
- acid solution
- fertilizer
- 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
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- Treating Waste Gases (AREA)
- Fertilizers (AREA)
Description
本発明は、有機化成肥料製造排ガスの脱臭法に
関する。さらに詳しくは、該肥料の造粒乾燥工程
からの排ガスをリン酸液で洗浄する該排ガスの脱
臭法に関する。
有機化成肥料すなわち、いわゆる化学肥料と天
然有機肥料とを湿式造粒および乾燥して得られる
肥料は、省力その他施肥合理化の観点から近年需
要が増加しつつある。
しかし、有機化成肥料の製造には悪臭の問題が
切離せないため、その製造時の排ガスの脱臭技術
が要望されている。
一般の脱臭技術の中、低濃度複合臭気に対して
は、通常湿式脱臭法が用いられ、脱臭剤として
は、酸、アルカリ、次亜塩素酸ナトリウム若しく
はグリオキザールその他の薬剤が用いられてい
る。しかしながら、本発明に係る有機化成肥料工
場の排ガスは、量が多いこと、炭酸ガスその
他種々の無臭及び有臭成分を含むこと、完全な
ダスト除去は事実上不可能であることなどから、
工業的に可能な脱臭法は未だ見出されていない。
本発明者等は、種々検討の結果、有機化成肥料
工場の排ガスを湿式法リン酸で洗浄すると、有効
に脱臭され、かつ、脱臭に使用した該リン酸は、
有機化成肥料の有効成分であるリン酸アンモニウ
ムの製造に支障なく使用し得ることを知つて本発
明を完成した。後述するようにリン酸に代えて、
硫酸、苛性ソーダ水溶液、次亜塩素酸ソーダ溶液
若しくは水を使用しても前記排ガス特有の複合臭
は除去されない。
これに反し、本発明の方法によれば、該複合臭
は除去され、代りにリン酸不純物臭が若干残る
が、この一次洗浄ガスは、水若しくは次亜塩素酸
ソーダ液で洗浄することにより、殆んど完全に除
去される。
以上の説明から明らかなように、本発明の目的
は、有機化成肥料製造排ガスの脱臭法を提供する
ことを目的とする。他の目的は、該使用ずみ排ガ
ス洗浄剤の処理法として特別な処理法を付加する
必要のない該脱臭法を提供することである。
本発明は、下記(1)の主要構成と(2)〜(3)の実施態
様的構成を有する。
(1) 有機化成肥料製造の最終工程である造粒乾燥
工程からの排ガスをリン酸液で洗浄することを
特徴とする有機化成肥料製造排ガスの脱臭法。
(2) 排ガス中のダストを分離した後リン酸液で洗
浄する前記第1項に記載の脱臭法。
(3) リン酸液として湿式法リン酸液を使用する前
記第1項に記載の脱臭法。
本発明の構成と効果につき以下に詳述する。
本発明に係る有機化成肥料とは、前述のように
いわゆる化学肥料例えば、硫酸アンモニウム、塩
化アンモニウム、硫酸カリウム、リン酸アンモニ
ウム、塩化カリウム、リン酸カリウム、尿素、2
−オキソ−4−メチル−6−ウレイドヘキサヒド
ロピリミジン、イソブチリデンジウレア若しくは
オキザミドのように有機無機を問わず、化学反応
によつて製造される肥料といわゆる天然肥料例え
ばナタネ粕、大豆粕、綿実粕のような搾油粕類、
魚粕、乾燥魚、魚菌体のような水産肥料、骨粉の
ような動物質肥料とを混合して造粒した肥料をい
う。また、有機化成肥料製造の最終工程である造
粒乾燥工程とは、公知の(複合)化成肥料の最終
工程とほゞ同様であつて、各肥効成分を所定量混
合し造粒器で造粒しついで乾燥する工程をいう。
該造粒乾燥工程からの排ガス(以下本発明に係
る排ガス)は、大部分空気、水蒸気、炭酸ガスお
よび少量の有機化成肥料からなるダストおよび本
発明の処理対象となる微量の悪臭成分からなる。
この排ガスをそのまゝ若しくは前述のダスト除
去後大気中に放出すると前述のように悪臭公害の
原因となる。
悪臭の化学成分は、こゝに特定し得ないが、一
般的に知られている低分子量のアミン類、メルカ
プタン類其他の複合したものであると考えられ
る。かゝる悪臭成分の本発明に係る排ガス中にお
ける濃度も有機化成肥料の製造条件により大巾に
変動すると考えられるが、数ppmから1000ppmの
範囲であると推察される。
本発明に使用するリン酸液は、後述の本発明に
係る排ガスの洗浄に適した濃度(H3PO4分とし
て5〜35重量%好ましくは10〜30重量%)であれ
ば、精製品であると工業用リン酸であるとを問わ
ず使用できる。一般には、いわゆる湿式法リン酸
が使用し易い。
本発明に係る排ガスのリン酸液による洗浄は特
定の液ガス接触方式に限定されないが、大量の該
排ガスに対して比較的少量の洗浄液を十分に接触
させるためには、後述のような気液向流接触方式
が望ましい。この洗浄方法の一態様を図によつて
説明する。図は、本発明方法の実施に使用する脱
臭装置のフローシートである。
空気ポンプ1に取込まれた空気は空気配管aを
経てヒーター2で例えば80℃まで加熱され加熱空
気配管bを経てニーダー3に供給される。ニーダ
ー3に予め仕込まれ加湿された有機化成肥料は、
捏和機による混合と温水ジヤケツト3′による加
熱とで悪臭を発生し、配管bから供給された加熱
空気により希釈されて悪臭ある排ガスとなる
(註、図の←A→の部分が悪臭発生装置である)。
ニーダー3を出た悪臭ガスは、配管cを経て第1
吸収塔4の塔底に入る。後述の実施例、比較例に
使用した該塔は、内径25cmψ充填部の高さ35cmで
該充填部には8mmψ×8mmhの磁性リングを充填
している。この吸収塔底に設けられたジヤケツト
5′付の吸収液タンク5には所定量の吸収液を伴
有し、吸収液ポンプ6および配管fを経て吸収液
を塔頂点にフイードし該塔内を通過して循環させ
る。第1吸収塔の運転条件は限定されないが、悪
臭ガス1Nlを通過させる間に吸収液を10〜200ml
好ましくは20〜100ml流下させる。悪臭ガスは、
造粒乾燥工程の廃ガスであるから温度は例えば50
〜100℃のように常温より相当高い。これに対し
て第1吸収塔の吸収液の温度は必ずしも合致させ
る必要はないが、悪臭ガスの熱を吸収して例えば
30〜70℃のような温度になる。
本発明の方法では、第1塔において前述のリン
酸液を吸収液として使用する。該塔で有機化成肥
料特有の臭気を殆んど除去された悪臭ガスは配管
dを経て第2吸収塔7の塔底に供給される。該塔
の形状、寸法は吸収塔1と同様であり、吸収液タ
ンク8、洗浄液ポンプ9および配管gを経て洗浄
液を塔7の塔頂にフイードして循環させる点は同
様である。
第2吸収塔では、第1塔のリン酸に代えて補助
的吸収剤例えば水若しくは次亜塩素酸ソーダの希
薄液(註、濃度100〜1000ppm)を使用して、第
1塔で処理された排ガス中のリン酸不純物臭を除
去する。ガス/液比は第1塔の場合とほゞ同様で
あり、処理温度は限定されないが第1塔を出た該
排ガスの温度30〜70℃から第2塔出口ガス温度と
して25〜55℃となる程度である。循環吸収液の温
度は当初室温のものが25〜50℃程度に上昇する。
該塔で処理された排ガスは配管eから排出され
る。以上述べた図の←B→部が悪臭除去装置であ
る。
工業的規模の装置においては、前述Aの悪臭発
生装置からの排ガス中のダストを公知のダストセ
パレーター、サイクロン等で除去したのち第1吸
収塔に供給することが望ましい。何故なら該ダス
トが第1塔の吸収液であるリン酸液に接触する
と、リン酸液の悪臭除去力が大巾に低下するから
である(註、後述実施例3参照)。
リン酸液および第2塔吸収液の脱臭力が維持さ
れているか否かは、図の装置の運転中排ガス試料
採取にS1、S2およびS3から各段階のガスを
経時的に採取して、脱臭力の著しく低下する以前
に夫々吸収液の一部若しくは全部を間歇的若しく
は連続的に置換する。置換された使用ずみリン酸
と吸収液は、アンモニア及び又は水酸化マグネシ
ウムで中和する等して有機化成肥料の製造に支障
なく利用することができ、その中和の際悪臭を発
生することはない(註、後述参考例1および2参
照)。
リン酸液による有機化成肥料排ガスの脱臭力
は、リン酸液の種類、濃度、洗浄条件、有機化成
肥料中の天然有機肥料の割合および造粒乾燥条件
によつて異るが、乾量基準で30重量%の天然有機
分を含む有機化成肥料1000gを製造するために30
%リン酸液10〜500ml好ましくは50〜200mlを必要
とする。したがつてP2O5分を化学肥料成分とし
て含有させた有機化成肥料であれば、そのP2O5
分の一部又は全部を上述の吸収処理ずみリン酸液
を中和して製造し混合することにより、「吸収処
理後のリン酸液」の処理を有機化成肥料製造以外
の処で別途考慮する必要がなくなる。
以下実施例および比較例によつて本発明を説明
する。
実施例1、比較例1〜4
図の装置を用い、ニーダー3に加湿した有機化
成肥料を入れ、該ニーダーに空気ポンプ1、ヒー
ター2を経由して加熱した空気を送つて悪臭ガス
を発生させ、該悪臭ガスを順次第1塔4および第
2塔7を通過させる間に夫々所定の洗浄剤(吸収
液)で洗浄して後排ガスとした。この間悪臭ガ
ス、1次洗浄ガスおよび排ガスの臭気の度合いを
官能試験により下記の4段階で評価した。
臭気の度合い
A:微かな臭気
B:弱い臭気
C:強い臭気
D:悪臭
ニーダー3に仕込んだものは有機化成肥料500
gで天然有機肥料として油粕と魚菌体の1:1
(重量比)混合物30重量%を含み、さらに150gの
水分を添加して加湿した混合物である。この混合
物を混和しながら、ジヤケツトに温水を通じて80
℃に加熱した。この間、前述の加熱空気を5/
分の速度で前記ニーダーに導入し、発生した悪臭
ガスは、第1塔4の塔底へ送つた。悪臭ガス、1
次洗浄ガスおよび排ガスの試料の採取は、採取口
S1、S2およびS3から行つた。
洗浄試験は、悪臭発生開始後2時間継続し、各
30分毎にS2およびS3のガスの臭気の度合いを
評価した。各塔は所定の吸収液(註、タンク5ま
たは6中の保有量各200ml)を150/分の速度
で、ポンプを用いて循環させた。
吸収液の種類と脱臭の程度を下表に示す。
The present invention relates to a method for deodorizing exhaust gas produced from organic chemical fertilizers. More specifically, the present invention relates to a method for deodorizing exhaust gas from the granulation and drying process of the fertilizer, in which the exhaust gas is washed with a phosphoric acid solution. Demand for organic chemical fertilizers, that is, fertilizers obtained by wet granulation and drying of so-called chemical fertilizers and natural organic fertilizers, has been increasing in recent years from the viewpoint of labor saving and other rationalization of fertilizer application. However, since the production of organic chemical fertilizers inevitably involves the problem of bad odors, there is a need for technology to deodorize the exhaust gas during production. Among general deodorizing techniques, a wet deodorizing method is usually used for low-concentration complex odors, and acids, alkalis, sodium hypochlorite, glyoxal, and other agents are used as deodorizing agents. However, the exhaust gas from the organic chemical fertilizer factory according to the present invention is large in volume, contains carbon dioxide and various other odorless and odorous components, and it is virtually impossible to completely remove dust.
An industrially possible deodorizing method has not yet been found. As a result of various studies, the present inventors have found that when exhaust gas from an organic chemical fertilizer factory is cleaned with wet phosphoric acid, it is effectively deodorized, and that the phosphoric acid used for deodorization is
The present invention was completed with the knowledge that it can be used without any problem in the production of ammonium phosphate, which is an active ingredient in organic chemical fertilizers. As described later, instead of phosphoric acid,
Even if sulfuric acid, aqueous caustic soda solution, sodium hypochlorite solution, or water is used, the complex odor characteristic of the exhaust gas cannot be removed. On the other hand, according to the method of the present invention, the complex odor is removed and a slight phosphoric acid impurity odor remains instead, but this primary cleaning gas can be cleaned with water or sodium hypochlorite solution. Almost completely removed. As is clear from the above description, an object of the present invention is to provide a method for deodorizing exhaust gas produced in organic chemical fertilizer production. Another object is to provide a deodorizing method that does not require any special treatment method for the used exhaust gas cleaning agent. The present invention has the following main configuration (1) and embodiment configurations (2) to (3). (1) A method for deodorizing exhaust gas from organic chemical fertilizer production, which is characterized by cleaning exhaust gas from the granulation and drying process, which is the final process of organic fertilizer manufacturing, with a phosphoric acid solution. (2) The deodorizing method according to item 1 above, wherein the dust in the exhaust gas is separated and then washed with a phosphoric acid solution. (3) The deodorizing method according to item 1 above, wherein a wet phosphoric acid solution is used as the phosphoric acid solution. The configuration and effects of the present invention will be explained in detail below. The organic compound fertilizer according to the present invention, as mentioned above, includes so-called chemical fertilizers such as ammonium sulfate, ammonium chloride, potassium sulfate, ammonium phosphate, potassium chloride, potassium phosphate, urea,
- Fertilizers produced by chemical reactions, whether organic or inorganic, such as oxo-4-methyl-6-ureidohexahydropyrimidine, isobutylidene diurea, or oxamide, and so-called natural fertilizers, such as rapeseed meal, soybean meal, and cotton. Oil extraction lees such as fruit lees,
A fertilizer made by mixing and granulating fish meal, dried fish, aquatic fertilizers such as fish bacteria, and animal fertilizers such as bone meal. In addition, the granulation and drying process, which is the final process of producing organic chemical fertilizer, is almost the same as the final process of known (composite) chemical fertilizers, in which a predetermined amount of each fertilizer ingredient is mixed and granulated using a granulator. This refers to the process of crushing and drying grains. The exhaust gas from the granulation and drying process (hereinafter referred to as the exhaust gas according to the present invention) mainly consists of air, water vapor, carbon dioxide gas, a small amount of organic compound fertilizer dust, and a trace amount of malodorous components that are treated by the present invention. If this exhaust gas is released into the atmosphere as it is or after the above-mentioned dust has been removed, it will cause foul odor pollution as mentioned above. Although the chemical component of the foul odor cannot be specifically identified, it is thought to be a complex of commonly known low molecular weight amines, mercaptans, and others. The concentration of such malodorous components in the exhaust gas according to the present invention is thought to vary widely depending on the manufacturing conditions of the organic compound fertilizer, but is estimated to be in the range of several ppm to 1000 ppm. The phosphoric acid solution used in the present invention may be a purified product as long as it has a concentration suitable for cleaning exhaust gas according to the present invention (described later) (5 to 35% by weight, preferably 10 to 30% by weight based on 4 minutes of H 3 PO). It can be used regardless of whether it is industrial phosphoric acid or not. Generally, the so-called wet phosphoric acid method is easy to use. The cleaning of exhaust gas with a phosphoric acid solution according to the present invention is not limited to a specific liquid-gas contact method, but in order to sufficiently contact a relatively small amount of cleaning liquid with a large amount of the exhaust gas, it is necessary to use a gas-liquid method as described below. A countercurrent contact method is preferred. One aspect of this cleaning method will be explained using figures. The figure is a flow sheet of a deodorizing device used to carry out the method of the present invention. Air taken into the air pump 1 passes through an air pipe a, is heated to, for example, 80°C by a heater 2, and is supplied to a kneader 3 via a heated air pipe b. The organic compound fertilizer that has been pre-loaded into the kneader 3 and humidified is
The mixing by the kneading machine and the heating by the hot water jacket 3' generate a foul odor, which is diluted by the heated air supplied from pipe b and becomes foul-smelling exhaust gas (Note: The part marked ←A→ in the diagram is the foul-smelling device). ).
The foul-smelling gas leaving the kneader 3 passes through the pipe c to the first
Enter the bottom of absorption tower 4. The column used in the Examples and Comparative Examples described later had an inner diameter of 25 cm ψ and a height of 35 cm in the packing section, and the packing section was filled with magnetic rings measuring 8 mm ψ x 8 mm h. An absorption liquid tank 5 with a jacket 5' provided at the bottom of the absorption tower contains a predetermined amount of absorption liquid, and the absorption liquid is fed to the top of the tower through an absorption liquid pump 6 and piping f, and the inside of the tower is Pass and circulate. The operating conditions of the first absorption tower are not limited, but 10 to 200 ml of absorption liquid is allowed to pass through 1Nl of malodorous gas.
Preferably 20 to 100 ml is allowed to flow down. The foul-smelling gas is
Since it is waste gas from the granulation drying process, the temperature is e.g.
~100℃, which is considerably higher than normal temperature. On the other hand, the temperature of the absorption liquid in the first absorption tower does not necessarily have to match, but it is possible to absorb the heat of the malodorous gas and
The temperature will be something like 30-70℃. In the method of the invention, the aforementioned phosphoric acid solution is used as an absorption liquid in the first column. The foul-smelling gas from which most of the odor characteristic of organic chemical fertilizers has been removed in the tower is supplied to the bottom of the second absorption tower 7 via pipe d. The shape and dimensions of this column are the same as those of the absorption column 1, and the washing liquid is fed to the top of the column 7 and circulated through the absorption liquid tank 8, the washing liquid pump 9, and the piping g. In the second absorption column, an auxiliary absorbent such as water or a dilute solution of sodium hypochlorite (note, concentration 100-1000 ppm) is used in place of the phosphoric acid in the first column. Removes phosphoric acid impurity odor from exhaust gas. The gas/liquid ratio is almost the same as in the case of the first column, and the treatment temperature is not limited, but the temperature of the exhaust gas exiting the first column is 30 to 70°C, and the gas temperature at the exit of the second column is 25 to 55°C. That's about it. The temperature of the circulating absorption liquid, initially at room temperature, rises to about 25-50°C.
The exhaust gas treated in the tower is discharged from pipe e. The part ←B→ in the diagram described above is the odor removal device. In an industrial-scale device, it is desirable to remove the dust in the exhaust gas from the malodor generating device A above using a known dust separator, cyclone, etc., and then supply it to the first absorption tower. This is because when the dust comes into contact with the phosphoric acid liquid, which is the absorption liquid in the first column, the odor removal ability of the phosphoric acid liquid is greatly reduced (see Example 3 below). Whether or not the deodorizing power of the phosphoric acid solution and the second column absorption liquid is maintained can be determined by sampling the exhaust gas at each stage from S1, S2, and S3 over time during operation of the device shown in the figure. Part or all of the absorbing liquid is replaced intermittently or continuously before the force drops significantly. The substituted used phosphoric acid and absorption liquid can be used without any problem in the production of organic chemical fertilizers by neutralizing them with ammonia and/or magnesium hydroxide, and no foul odor will be generated during the neutralization. (Note, see Reference Examples 1 and 2 below). The deodorizing power of organic compound fertilizer exhaust gas with phosphoric acid solution varies depending on the type of phosphoric acid solution, concentration, cleaning conditions, proportion of natural organic fertilizer in organic compound fertilizer, and granulation drying conditions, but on a dry basis. 30 to produce 1000g of organic fertilizer containing 30% by weight of natural organic content.
% phosphoric acid solution 10-500ml, preferably 50-200ml is required. Therefore, if it is an organic chemical fertilizer that contains P 2 O 5 as a chemical fertilizer component, the P 2 O 5
By neutralizing and mixing part or all of the above-mentioned absorption-treated phosphoric acid solution, the treatment of the "absorption-treated phosphoric acid solution" can be considered separately in a place other than organic fertilizer production. There will be no need. The present invention will be explained below with reference to Examples and Comparative Examples. Example 1, Comparative Examples 1 to 4 Using the apparatus shown in the figure, humidified organic chemical fertilizer was placed in a kneader 3, and heated air was sent to the kneader via an air pump 1 and a heater 2 to generate malodorous gas. While the malodorous gas was sequentially passed through the first column 4 and the second column 7, it was washed with a predetermined cleaning agent (absorbing liquid), respectively, to obtain a post-exhaust gas. During this time, the degree of odor of the malodorous gas, primary cleaning gas, and exhaust gas was evaluated by a sensory test on the following four levels. Degree of odor A: Slight odor B: Weak odor C: Strong odor D: Bad odor The material charged in kneader 3 is organic compound fertilizer 500
1:1 of oil cake and fish bacteria as a natural organic fertilizer
The mixture contains 30% by weight (weight ratio) and is further humidified by adding 150g of water. While mixing, pass this mixture through a jacket of warm water for 80 minutes.
heated to ℃. During this time, the heated air mentioned above was
The malodorous gas generated was sent to the bottom of the first column 4. foul-smelling gas, 1
Samples of the next cleaning gas and exhaust gas were collected from sampling ports S1, S2, and S3. The cleaning test continued for 2 hours after the onset of odor, and
The degree of odor of gases S2 and S3 was evaluated every 30 minutes. Each column was circulated with a pump at a rate of 150/min with a given absorption liquid (note: 200 ml each in tank 5 or 6). The table below shows the type of absorbent and the degree of deodorization.
【表】
表に明らかなように、第1塔で有効な吸収剤を
使用すれば、第2塔は水洗で十分である。硫酸、
苛性ソーダ又は次亜塩素酸ソーダによる洗浄では
天然有機肥料特有の複合臭を除去できない。
実施例 2
ニーダー3中の加湿した有機化成肥料を2時間
後に新たに入れ替えた以外は同様に実施した。そ
の結果、リン酸吸収液の脱臭能力は、該有機化成
肥料の2バツチ分まで維持できることが判つた。
参考例 1
実施例2で悪臭吸収力が限界に達したリン酸
100mlを採り、アンモニア水を加えてPH7.0まで中
和した。ついで該中和物を80℃に加熱し、少量の
空気を吹込んで排気中の臭気を実施例1と同様に
判定した。この臭気は、リン酸不純物臭で臭気の
程度はBであつた。
参考例 2
実施例2で悪臭吸収力が限界に達したリン酸
100mlを採り、当量のアンモニア水と水酸化マグ
ネシウムを加えて反応させ、リン酸マグネシウム
アンモニウムを生成させた。以後参考例1と同様
に空気吹込試験を行つたが、臭気の程度および内
容は参考例1の場合と同様であつた。参考例1お
よび2の結果は、悪臭吸収力が限界に達したリン
酸を化成肥料の原料としても天然有機肥料の悪臭
が再生されることはないことを示している。
実施例 3
実施例1で使用した湿式法リン酸液に代えてリ
ン酸分の0.2、1および5重量%の有機化成肥料
(註、実施例1で使用したもの)を混合して分散
ないし溶解させたものを使用した以外は同様にし
て排ガス脱臭を行つた。その結果、上述の0.2重
量%添加の場合でも脱臭効果は明白に低下した。
この結果は、有機化成肥料の造粒乾燥工程の排
ガスは本発明に係る脱臭処理前に該排ガス中のダ
ストを除去してから該処理をされるべきであるこ
とを示している。
実施例 4
実施例1で供給した空気に代えて、化成肥料造
粒乾燥工程(註、天然有機肥料を含まず)の排ガ
スを用いた以外は同様に実施した。リン酸液の脱
臭力には変化がなかつた。この結果は、リン酸液
の脱臭力は化成肥料造粒工程の排ガスによつては
低下しないことを示している。[Table] As is clear from the table, if an effective absorbent is used in the first column, water washing is sufficient for the second column. sulfuric acid,
Cleaning with caustic soda or sodium hypochlorite cannot remove the complex odor characteristic of natural organic fertilizers. Example 2 The same procedure was carried out except that the humidified organic compound fertilizer in the kneader 3 was replaced after 2 hours. As a result, it was found that the deodorizing ability of the phosphoric acid absorption liquid could be maintained up to two batches of the organic compound fertilizer. Reference Example 1 Phosphoric acid whose bad odor absorption capacity reached its limit in Example 2
100ml was taken and ammonia water was added to neutralize it to pH 7.0. The neutralized product was then heated to 80°C, a small amount of air was blown into it, and the odor in the exhaust gas was evaluated in the same manner as in Example 1. This odor was a phosphoric acid impurity odor and the odor level was B. Reference Example 2 Phosphoric acid whose bad odor absorption capacity reached its limit in Example 2
100 ml was taken, and equivalent amounts of aqueous ammonia and magnesium hydroxide were added and reacted to produce magnesium ammonium phosphate. Thereafter, an air blowing test was conducted in the same manner as in Reference Example 1, and the degree and content of the odor were the same as in Reference Example 1. The results of Reference Examples 1 and 2 show that even if phosphoric acid, whose malodor absorption capacity has reached its limit, is used as a raw material for chemical fertilizers, the malodor of natural organic fertilizers will not be regenerated. Example 3 Instead of the wet method phosphoric acid solution used in Example 1, organic chemical fertilizers with a phosphoric acid content of 0.2, 1, and 5% by weight (note, the one used in Example 1) were mixed and dispersed or dissolved. Exhaust gas deodorization was carried out in the same manner except that the same method was used. As a result, even in the case of addition of 0.2% by weight, the deodorizing effect clearly decreased. This result indicates that the exhaust gas from the granulation and drying process of organic chemical fertilizer should be treated after removing dust from the exhaust gas before the deodorizing treatment according to the present invention. Example 4 The same procedure was carried out as in Example 1, except that the air supplied in Example 1 was replaced with exhaust gas from the chemical fertilizer granulation and drying process (note: no natural organic fertilizer was included). There was no change in the deodorizing power of the phosphoric acid solution. This result shows that the deodorizing power of the phosphoric acid solution is not reduced by the exhaust gas from the chemical fertilizer granulation process.
図は、本発明の方法に使用する脱臭装置のフロ
ーシートを示す。
図中、1……空気ポンプ、6,9……洗浄液ポ
ンプ、2……ヒーター、3……ニーダー、5,8
……タンク、4……洗浄第1塔、7……洗浄第2
塔、S1、S2、S3……ガス試料採取口。
The figure shows a flow sheet of a deodorizing device used in the method of the invention. In the figure, 1... Air pump, 6, 9... Cleaning liquid pump, 2... Heater, 3... Kneader, 5, 8
...Tank, 4...Washing 1st tower, 7...Washing 2nd
Tower, S1, S2, S3...Gas sampling ports.
Claims (1)
工程からの排ガスをリン酸液で洗浄後、ひきつづ
き水又は次亜塩素酸ナトリウム水溶液で洗浄する
ことを特徴とする有機化成肥料製造排ガスの脱臭
法。 2 排ガス中のダストを分離した後リン酸液で洗
浄する特許請求の範囲第1項に記載の脱臭法。 3 リン酸液として湿式法リン酸液を使用する特
許請求の範囲第1項に記載の脱臭法。[Claims] 1. An organic chemical compound characterized in that the exhaust gas from the granulation drying step, which is the final step in the production of organic compound fertilizer, is washed with a phosphoric acid solution and then subsequently washed with water or an aqueous sodium hypochlorite solution. Deodorizing method for fertilizer manufacturing exhaust gas. 2. The deodorizing method according to claim 1, wherein the dust in the exhaust gas is separated and then washed with a phosphoric acid solution. 3. The deodorizing method according to claim 1, wherein a wet phosphoric acid solution is used as the phosphoric acid solution.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP58160673A JPS6051530A (en) | 1983-09-01 | 1983-09-01 | Method for deodorizing exhaust gas from organic compound fertilizer preparing process |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP58160673A JPS6051530A (en) | 1983-09-01 | 1983-09-01 | Method for deodorizing exhaust gas from organic compound fertilizer preparing process |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS6051530A JPS6051530A (en) | 1985-03-23 |
| JPH0440055B2 true JPH0440055B2 (en) | 1992-07-01 |
Family
ID=15720002
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP58160673A Granted JPS6051530A (en) | 1983-09-01 | 1983-09-01 | Method for deodorizing exhaust gas from organic compound fertilizer preparing process |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS6051530A (en) |
Families Citing this family (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH01151924A (en) * | 1987-12-08 | 1989-06-14 | Yonemi Tanaka | Treatment of organic waste gas such as chicken-droppings |
| JPH04123244U (en) * | 1991-04-11 | 1992-11-06 | 日立精機株式会社 | Hardening coil position measurement correction device for induction hardening equipment |
| JP5467765B2 (en) * | 2008-12-18 | 2014-04-09 | 住化エンビロサイエンス株式会社 | Fertilizer manufacturing method |
| KR100911176B1 (en) | 2009-03-09 | 2009-08-06 | 한경대학교 산학협력단 | Odor treatment method and device generated in manure using animal manure |
| CN103007716A (en) * | 2012-12-22 | 2013-04-03 | 山东博丰利众化工有限公司 | Recycling device for dilute acid in pyrite acid making purification |
Family Cites Families (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5165099A (en) * | 1974-12-04 | 1976-06-05 | Mitsui Toatsu Chemicals | RINANGANJUHIRYONO SEIZOHOHO |
-
1983
- 1983-09-01 JP JP58160673A patent/JPS6051530A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS6051530A (en) | 1985-03-23 |
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