JPH09227493A - Recovery of urea dust and ammonia from exhaust gas - Google Patents

Recovery of urea dust and ammonia from exhaust gas

Info

Publication number
JPH09227493A
JPH09227493A JP3955196A JP3955196A JPH09227493A JP H09227493 A JPH09227493 A JP H09227493A JP 3955196 A JP3955196 A JP 3955196A JP 3955196 A JP3955196 A JP 3955196A JP H09227493 A JPH09227493 A JP H09227493A
Authority
JP
Japan
Prior art keywords
urea
ammonia
dust
acid
exhaust gas
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
JP3955196A
Other languages
Japanese (ja)
Inventor
Hidetsugu Fujii
英嗣 藤井
Haruyuki Morikawa
晴行 森川
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.)
Toyo Engineering Corp
Original Assignee
Toyo Engineering Corp
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Toyo Engineering Corp filed Critical Toyo Engineering Corp
Priority to JP3955196A priority Critical patent/JPH09227493A/en
Publication of JPH09227493A publication Critical patent/JPH09227493A/en
Pending legal-status Critical Current

Links

Abstract

PROBLEM TO BE SOLVED: To clean exhaustion gas by simultaneously recovering urea and ammonia from exhaust gas containing urea dust and ammonia. SOLUTION: When urea and ammonia are recovered by bringing a gas containing urea dust and ammonia into contact with an aqueous urea solution, an aqueous urea solution with a pH of 3.5-5.5 is used.

Description

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

【0001】[0001]

【発明の属する技術分野】本発明は尿素ダスト及びアン
モニアを含むガスから尿素及びアンモニアを回収し、ガ
スを清浄化する方法に属する。
TECHNICAL FIELD The present invention relates to a method for recovering urea and ammonia from a gas containing urea dust and ammonia and cleaning the gas.

【0002】[0002]

【従来の技術】尿素及びアンモニアを含むガスには尿素
プラントの濃縮器、プリル尿素造粒塔、流動層を用いた
尿素造粒塔あるいは化成肥料製造プラントの排気ガス等
がある。例えば、プリル尿素製造に用いられる造粒塔で
は塔頂部から落下する尿素液滴を空気にて冷却させ固化
させている。冷却に使われた空気は造粒塔頂部から排出
されるが、この排出空気には尿素のダスト、溶融尿素に
含まれ固化とともに冷却され空気中に放たれたアンモニ
アが含まれる。その濃度は造粒塔の大きさ、溶融尿素の
分散設備により異なるが、一般には尿素ダスト70〜200
mg/Nm3 、アンモニア50〜150 mg/Nm3 の範囲にある。
噴流層若しくは流動層内で尿素溶液を噴霧し造粒する大
粒尿素製造方法においても尿素の固化熱は造粒器にある
流動層、噴流層部分で空気によって除去する。これらの
造粒器からの尿素粒は温度が90〜110 ℃と高いので空気
により粒子を冷却するために別途設けた流動層冷却器に
よってさらに取り扱いやすい温度、例えば70〜80℃まで
冷却される。これら造粒器、流動層冷却器からの排出空
気にはやはり尿素ダスト、アンモニアが含まれる。この
方法では、造粒塔方式に比べ造粒器内の空気速度が速い
ため、尿素のダスト濃度は5000〜15000 mg/Nm3 と高
く、アンモニア濃度も空気量が造粒塔法に比べ少ないの
でその濃度は高く 100〜500mg /Nm3 である。ドラム、
皿型造粒法による造粒においても、冷却用の空気が必要
で、冷却後の空気には尿素ダスト、アンモニアが同様に
含まれる。これらの設備から排出される空気は、上述の
通り尿素ダスト、アンモニアを相当量含むためそのまま
では排出できず回収設備にて処理した後排出しなければ
ならない。尿素ダストの回収については、充填塔内で循
環する希薄な尿素水溶液と接触させて回収する技術があ
り、尿素は20〜50mg/Nm3 の濃度まで低下できる。
2. Description of the Related Art Gases containing urea and ammonia include a concentrator of a urea plant, a prill urea granulating tower, a urea granulating tower using a fluidized bed or an exhaust gas of a chemical fertilizer manufacturing plant. For example, in a granulation tower used for prill urea production, urea droplets falling from the top of the tower are cooled with air and solidified. The air used for cooling is discharged from the top of the granulation tower, and the discharged air contains urea dust, ammonia contained in molten urea, which is cooled as it solidifies and is released into the air. The concentration varies depending on the size of the granulation tower and the equipment for dispersing molten urea, but generally urea dust 70-200
It is in the range of mg / Nm 3 and ammonia 50 to 150 mg / Nm 3 .
Also in the large-sized urea production method in which a urea solution is sprayed and granulated in a spouted bed or a fluidized bed, the heat of solidification of urea is removed by air in the fluidized bed and the spouted bed in the granulator. Since the temperature of urea particles from these granulators is as high as 90 to 110 ° C, it is further cooled to a temperature which is easy to handle, for example 70 to 80 ° C, by a fluidized bed cooler separately provided for cooling the particles by air. The air discharged from these granulators and fluidized bed coolers also contains urea dust and ammonia. In this method, the air velocity in the granulator is faster than in the granulation tower method, so the dust concentration of urea is as high as 5000 to 15000 mg / Nm 3 , and the ammonia concentration is also smaller than in the granulation tower method, so Its concentration is high, 100-500 mg / Nm 3 . drum,
Even in the granulation by the plate-type granulation method, cooling air is necessary, and the cooled air also contains urea dust and ammonia. The air discharged from these facilities cannot be discharged as it is because it contains a considerable amount of urea dust and ammonia as described above, and must be discharged after being treated by the recovery facility. Regarding the recovery of urea dust, there is a technology of contacting with a dilute aqueous urea solution circulating in a packed column to recover urea, and urea can be reduced to a concentration of 20 to 50 mg / Nm 3 .

【0003】[0003]

【発明が解決しようとする課題】しかし、アンモニアの
尿素水溶液への溶解度は非常に小さくほとんど吸収され
ず、上記の高い濃度のままアンモニアが放出され環境汚
染の一つとなっている。本発明は、尿素ダストとアンモ
ニアを同時に回収し排出ガスを清浄化する手段の提供に
ある。
However, the solubility of ammonia in the urea aqueous solution is very small and hardly absorbed, and ammonia is released at the above high concentration, which is one of environmental pollution. The present invention provides a means for simultaneously recovering urea dust and ammonia and cleaning exhaust gas.

【0004】[0004]

【課題を解決するための手段】本発明は、尿素ダスト及
びアンモニアを含むガスを尿素水溶液に接触させ尿素を
回収する方法において、前記尿素水溶液のpHを 3.5〜5.
5 とすることを特徴とする尿素ダスト及びアンモニアの
回収方法である。さらに本発明は、上記尿素水溶液のpH
を 3.5〜5.5 に保つため、酸として硝酸、塩酸、硫酸、
燐酸の何れか1乃至複数を組み合わせて使用する方法を
含む。
The present invention is a method for recovering urea by bringing a gas containing urea dust and ammonia into contact with an aqueous urea solution to obtain a urea solution having a pH of 3.5 to 5.
The method for recovering urea dust and ammonia is characterized in that Furthermore, the present invention provides the pH of the urea aqueous solution.
Nitric acid, hydrochloric acid, sulfuric acid,
It includes a method of using any one or more of phosphoric acid in combination.

【0005】[0005]

【発明の実施の形態】以下、本発明について詳細に説明
する。図1は、尿素ダスト及びアンモニアを含む排ガス
の発生源の一例として尿素の造粒器を含む本発明の尿素
ダスト及びアンモニアの回収方法を示す概念図である。
尿素合成の濃縮工程からの尿素は溶融状態でライン11を
経由して尿素の造粒器1に送られ尿素粒子としてライン
13から送り出される。溶融尿素の固化熱を除去する目的
に使用される空気はライン12を経由して造粒器1に導入
される。冷却に使われた空気は造粒器からライン14を経
由して排出されるが、その排出空気には造粒形式、造粒
条件により尿素ダスト、アンモニアがそれぞれ5000〜15
000 mg/Nm3 、 100〜500 mg/Nm3 が含まれる。排出空
気は大気汚染をさけるためライン14を経由して排気洗浄
設備2に送られる。排気洗浄設備2は尿素水溶液を充填
層に循環し、充填層内で尿素水溶液と排出空気とが接触
する間に含まれる尿素ダストを回収する。尿素水溶液で
はアンモニアは除去できないため酸を加え尿素水溶液の
pHを 3.5〜5.5 に保ち排出ガスに含まれるアンモニアを
併せて回収する。pH 3.5〜5.5 に保つために使用する酸
の種類は特に制限はないが、硝酸、塩酸、燐酸及び硫酸
がアンモニアとの反応で生成する塩は、それぞれ硝酸ア
ンモニウム、塩化アンモニウム、燐酸アンモニウム及び
硫酸アンモニウムとなり何れも窒素肥料となるためより
好ましい。例えば酸として硝酸を使用する場合、尿素水
溶液循環液中の尿素及び硝酸アンモニウムの濃度があが
らないよう循環液の一部はライン17を経由して抜き出さ
れる。抜き出された循環水は、いわゆるUAN(尿素−
硝酸アンモニウム水溶液)であり、濃縮して液体肥料と
して使用される。循環水の補充のための水とpHを所定範
囲に保つための酸はそれぞれライン15及びライン16にて
排気洗浄設備2に供給される。循環尿素水溶液のpHが
5.5を超えると排気洗浄設備2の循環水中に酸がなくア
ンモニア過剰の液になるので酸とアンモニアとの反応が
不十分となりアンモニアを吸収する能力が小さくなり効
果が得られない。
BEST MODE FOR CARRYING OUT THE INVENTION The present invention will be described in detail below. FIG. 1 is a conceptual diagram showing a urea dust and ammonia recovery method of the present invention including a urea granulator as an example of a source of an exhaust gas containing urea dust and ammonia.
Urea from the concentration step of the urea synthesis is sent to the urea granulator 1 via the line 11 in the molten state and is fed as urea particles into the line.
Sent out from 13. The air used for the purpose of removing the heat of solidification of the molten urea is introduced into the granulator 1 via the line 12. The air used for cooling is discharged from the granulator through line 14, and the discharged air contains urea dust and ammonia of 5000 to 15 depending on the granulation type and granulation conditions.
000 mg / Nm 3 and 100-500 mg / Nm 3 are included. The exhausted air is sent to the exhaust cleaning equipment 2 via a line 14 to avoid air pollution. The exhaust gas cleaning facility 2 circulates the urea aqueous solution in the packed bed, and recovers the urea dust contained during the contact between the urea aqueous solution and the exhaust air in the packed bed. Ammonia cannot be removed with urea solution, so acid is added
Keep the pH at 3.5-5.5 and also collect the ammonia contained in the exhaust gas. The type of acid used to maintain pH 3.5 to 5.5 is not particularly limited, but the salts produced by the reaction of nitric acid, hydrochloric acid, phosphoric acid and sulfuric acid with ammonia are ammonium nitrate, ammonium chloride, ammonium phosphate and ammonium sulfate, respectively. Is more preferable because it also becomes a nitrogen fertilizer. For example, when nitric acid is used as the acid, a part of the circulating liquid is extracted via line 17 so that the concentrations of urea and ammonium nitrate in the urea aqueous solution circulating liquid do not rise. The circulating water extracted is the so-called UAN (urea-
Aqueous ammonium nitrate solution), which is concentrated and used as liquid fertilizer. Water for supplementing the circulating water and acid for keeping the pH within a predetermined range are supplied to the exhaust cleaning equipment 2 via lines 15 and 16, respectively. The pH of the circulating urea solution is
If it exceeds 5.5, there is no acid in the circulating water of the exhaust gas cleaning facility 2 and a liquid with excess ammonia is formed, and the reaction between the acid and ammonia is insufficient, and the ability to absorb ammonia is reduced, and no effect can be obtained.

【0006】一方、pHが 3.5未満では循環水中に残留す
る酸が多くなり、抜き出した液中の酸を固定するための
アンモニアの量が増加し運転費の増加をもたらす。こう
して排気洗浄設備で排ガス中に含まれる尿素ダスト、ア
ンモニアはそれぞれ50mg/Nm3 以下まで吸収除去されラ
イン18にて大気中に放出される。尿素ダストとアンモニ
アを含む排ガスとpH 3.5〜5.5 に調節された尿素水溶液
との接触は充填塔方式に拘らずベンチュリー方式でも可
能である。本発明は、ガスと液を接触させる形式のもの
全てに適用可能である。
On the other hand, when the pH is less than 3.5, a large amount of acid remains in the circulating water, the amount of ammonia for fixing the acid in the extracted liquid increases, and the operating cost increases. In this way, the urea dust and ammonia contained in the exhaust gas are absorbed and removed to 50 mg / Nm 3 or less in the exhaust gas cleaning facility, and are released into the atmosphere through the line 18. The exhaust gas containing urea dust and ammonia and the aqueous urea solution adjusted to pH 3.5 to 5.5 can be contacted by the venturi method regardless of the packed column method. INDUSTRIAL APPLICABILITY The present invention can be applied to all types in which gas and liquid are brought into contact with each other.

【0007】[0007]

【作用】尿素水溶液をpH 3.5〜5.5 として使用するため
の尿素の吸収のみならずアンモニアの吸収も併せて可能
となる。
[Function] It is possible to absorb not only urea but also ammonia for using the aqueous urea solution at pH 3.5 to 5.5.

【0008】[0008]

【実施例】以下、実施例により本発明を更に具体的に説
明するが、本発明はこれに限定されるものではない。 実施例1 尿素粒子製造能力50t/hの造粒塔にて冷却用空気を18
0000 Nm3/h使用した場合に本発明を適用した。この冷
却用空気が造粒器から排出されるとき尿素ダスト2160kg
/h(12000 mg/Nm3)、アンモニア90kg/h(500 mg/
Nm3)を含んでいた。この空気を尿素水溶液循環液量が 1
80t/hで回っている充填塔である排気洗浄設備に導入
した。排気洗浄設備には尿素水溶液のpHが 4.5になるよ
うに硝酸310kg/hを供給した。排気洗浄設備から回収
した尿素、硝酸アンモニウムの水溶液濃度が40%になる
よう、排出される空気に含まれる蒸気として排出される
水の補給を併せて水を 13360kg/h排気洗浄設備に供給
した。この時回収した水溶液は8920kg/hであった。排
気洗浄塔から排出された空気には尿素ダスト、アンモニ
アがそれぞれ7kg/h(39mg/Nm3)含まれていた。 比較例1 実施例1の条件でpHを 6.5にしたとき硝酸は 133kg/h
の量であった。この時、排気洗浄設備から排出された空
気中の尿素ダストは7kg/h(39mg/Nm3)と低い値を示
したがアンモニアは54kg/h(300 mg/Nm3)であった。 比較例2 実施例1の条件でpHを 3.0にしたとき硝酸は 537kg/h
の量であった。この時、排気洗浄設備から排出された空
気中の尿素ダストおよびアンモニアはそれぞれ7kg/h
(39mg/Nm3)、5kg/h(28mg/Nm3)、と低い値を示し
たが、回収溶液中に33kg/hの硝酸が含まれており硝酸
アンモニウムとして固定するには9kg/hのアンモニア
が別途必要であった。
EXAMPLES The present invention will be described in more detail with reference to the following Examples, but it should not be construed that the present invention is limited thereto. Example 1 Cooling air was supplied to a granulation tower with a urea particle production capacity of 50 t / h at a temperature of 18
The present invention was applied when 0000 Nm 3 / h was used. When this cooling air is discharged from the granulator, urea dust 2160kg
/ H (12000 mg / Nm 3 ), ammonia 90 kg / h (500 mg /
Nm 3 ) was included. The amount of this urea air circulating fluid is 1
It was introduced into the exhaust cleaning equipment, which is a packed tower rotating at 80 t / h. To the exhaust gas cleaning equipment, 310 kg / h of nitric acid was supplied so that the pH of the urea aqueous solution would be 4.5. Water was supplied to the exhaust cleaning facility at 13360 kg / h together with the replenishment of water discharged as vapor contained in the discharged air so that the concentration of urea and ammonium nitrate solution recovered from the exhaust cleaning facility became 40%. The aqueous solution recovered at this time was 8920 kg / h. The air discharged from the exhaust cleaning tower contained urea dust and ammonia of 7 kg / h (39 mg / Nm 3 ), respectively. Comparative Example 1 When the pH was adjusted to 6.5 under the conditions of Example 1, nitric acid was 133 kg / h.
Was the amount. At this time, urea dust in the air discharged from the exhaust gas cleaning equipment showed a low value of 7 kg / h (39 mg / Nm 3 ), but ammonia was 54 kg / h (300 mg / Nm 3 ). Comparative Example 2 When the pH was adjusted to 3.0 under the conditions of Example 1, nitric acid was 537 kg / h.
Was the amount. At this time, urea dust and ammonia in the air discharged from the exhaust cleaning equipment were 7 kg / h each.
(39 mg / Nm 3 ), 5 kg / h (28 mg / Nm 3 ), which was a low value, but the recovery solution contained 33 kg / h nitric acid, and 9 kg / h ammonia was used to fix it as ammonium nitrate. Was required separately.

【0009】[0009]

【発明の効果】本発明は、排気ガス中に含まれる尿素ダ
ストとアンモニアを尿素水溶液に吸収するために尿素水
溶液をpH 3.5〜5.5 としているために尿素ダストのみな
らずアンモニアも同時に吸収回収できる。又、酸として
硝酸、塩酸、硫酸、燐酸の中から選ばれた酸を使用した
場合は、回収された尿素水溶液を濃縮して液体肥料とし
て使用できるという利点もある。
According to the present invention, since the urea aqueous solution has a pH of 3.5 to 5.5 in order to absorb the urea dust and ammonia contained in the exhaust gas into the urea aqueous solution, not only urea dust but also ammonia can be absorbed and recovered at the same time. Further, when an acid selected from nitric acid, hydrochloric acid, sulfuric acid and phosphoric acid is used as the acid, there is an advantage that the recovered urea aqueous solution can be concentrated and used as a liquid fertilizer.

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

【図1】本発明の排ガスに含まれる尿素ダスト及びアン
モニアを回収する方法の概念図である。
FIG. 1 is a conceptual diagram of a method for recovering urea dust and ammonia contained in exhaust gas according to the present invention.

【符号の説明】[Explanation of symbols]

1 造粒器 2 排気洗浄設備 1 Granulator 2 Exhaust cleaning equipment

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 尿素ダスト及びアンモニアを含むガスを
尿素水溶液に接触させ尿素を回収する方法において、前
記尿素水溶液のpHを 3.5〜5.5 とすることを特徴とする
尿素ダスト及びアンモニアの回収方法。
1. A method for recovering urea by bringing a gas containing urea dust and ammonia into contact with an aqueous urea solution, wherein the pH of the aqueous urea solution is 3.5 to 5.5.
【請求項2】 尿素水溶液のpHを 3.5〜5.5 に保つた
め、酸として硝酸、塩酸、硫酸、燐酸の何れか1乃至複
数を組み合わせて使用することを特徴とする請求項1記
載の尿素ダスト及びアンモニアの回収方法。
2. The urea dust according to claim 1, wherein any one or more of nitric acid, hydrochloric acid, sulfuric acid and phosphoric acid is used as an acid in order to keep the pH of the aqueous urea solution at 3.5 to 5.5. Ammonia recovery method.
JP3955196A 1996-02-27 1996-02-27 Recovery of urea dust and ammonia from exhaust gas Pending JPH09227493A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP3955196A JPH09227493A (en) 1996-02-27 1996-02-27 Recovery of urea dust and ammonia from exhaust gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP3955196A JPH09227493A (en) 1996-02-27 1996-02-27 Recovery of urea dust and ammonia from exhaust gas

Publications (1)

Publication Number Publication Date
JPH09227493A true JPH09227493A (en) 1997-09-02

Family

ID=12556208

Family Applications (1)

Application Number Title Priority Date Filing Date
JP3955196A Pending JPH09227493A (en) 1996-02-27 1996-02-27 Recovery of urea dust and ammonia from exhaust gas

Country Status (1)

Country Link
JP (1) JPH09227493A (en)

Cited By (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007507333A (en) * 2003-10-02 2007-03-29 ウーデ・ゲゼルシヤフト・ミツト・ベシユレンクテル・ハフツング A method for removing ammonia and dust from waste gas produced in the production of chemical fertilizers.
WO2011032786A1 (en) 2009-09-16 2011-03-24 Dsm Ip Assets B.V. Removal of urea and ammonia from exhaust gases
EP2386346A1 (en) 2010-05-11 2011-11-16 Stamicarbon B.V. Process for the reduction of ammonia emissions in a urea manufacturing process
JP2012509833A (en) * 2008-11-28 2012-04-26 ウーデ・フェルティリツァー・テヒノロギー・ベスローテン・フェンノートシャップ Urea granulation with an acidic scrubbing system and subsequent incorporation of ammonium salts into urea granules
WO2018122377A1 (en) 2016-12-30 2018-07-05 Yara International Asa Processing of exhaust gases from a urea plant
WO2018122379A1 (en) 2016-12-30 2018-07-05 Yara International Asa Method for processing a gas stream comprising urea dust and ammonia
WO2018168573A1 (en) * 2017-03-17 2018-09-20 東洋エンジニアリング株式会社 Method for granulating urea
JP2019098307A (en) * 2017-12-08 2019-06-24 東洋エンジニアリング株式会社 Method and apparatus for treating aqueous solution containing urea, ammonia and carbon dioxide
CN110496516A (en) * 2019-09-24 2019-11-26 福建龙净环保股份有限公司 A kind of urea prilling tower removes ammonia system
WO2019234816A1 (en) * 2018-06-05 2019-12-12 三菱重工エンジニアリング株式会社 Fertilizer production plant and fertilizer production method

Cited By (20)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2007507333A (en) * 2003-10-02 2007-03-29 ウーデ・ゲゼルシヤフト・ミツト・ベシユレンクテル・ハフツング A method for removing ammonia and dust from waste gas produced in the production of chemical fertilizers.
JP2012509833A (en) * 2008-11-28 2012-04-26 ウーデ・フェルティリツァー・テヒノロギー・ベスローテン・フェンノートシャップ Urea granulation with an acidic scrubbing system and subsequent incorporation of ammonium salts into urea granules
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