JPS5850785B2 - How to dry nitrate solution - Google Patents

How to dry nitrate solution

Info

Publication number
JPS5850785B2
JPS5850785B2 JP9996476A JP9996476A JPS5850785B2 JP S5850785 B2 JPS5850785 B2 JP S5850785B2 JP 9996476 A JP9996476 A JP 9996476A JP 9996476 A JP9996476 A JP 9996476A JP S5850785 B2 JPS5850785 B2 JP S5850785B2
Authority
JP
Japan
Prior art keywords
nitrate
particle size
spray
nitrate solution
drying
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
Application number
JP9996476A
Other languages
Japanese (ja)
Other versions
JPS5325266A (en
Inventor
勝 三田
彰 山本
健三郎 児玉
昇助 富永
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.)
Kawasaki Heavy Industries Ltd
Original Assignee
Kawasaki Heavy Industries Ltd
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 Kawasaki Heavy Industries Ltd filed Critical Kawasaki Heavy Industries Ltd
Priority to JP9996476A priority Critical patent/JPS5850785B2/en
Publication of JPS5325266A publication Critical patent/JPS5325266A/en
Publication of JPS5850785B2 publication Critical patent/JPS5850785B2/en
Expired legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C01INORGANIC CHEMISTRY
    • C01FCOMPOUNDS OF THE METALS BERYLLIUM, MAGNESIUM, ALUMINIUM, CALCIUM, STRONTIUM, BARIUM, RADIUM, THORIUM, OR OF THE RARE-EARTH METALS
    • C01F11/00Compounds of calcium, strontium, or barium
    • C01F11/36Nitrates
    • C01F11/44Concentrating; Crystallisating; Dehydrating; Preventing the absorption of moisture or caking

Landscapes

  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Geology (AREA)
  • Inorganic Chemistry (AREA)
  • Compounds Of Alkaline-Earth Elements, Aluminum Or Rare-Earth Metals (AREA)
  • Heat Treatment Of Water, Waste Water Or Sewage (AREA)
  • Vaporization, Distillation, Condensation, Sublimation, And Cold Traps (AREA)
  • Physical Or Chemical Processes And Apparatus (AREA)

Description

【発明の詳細な説明】 本発明は廃棄処理を必要とする硝酸カルシウム水溶液な
どの硝酸塩溶液、または湿式脱硝処理の際副生ずる硝酸
カルシウム水溶液などの硝酸塩を主成分とする溶液など
の乾燥方法に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for drying a nitrate solution such as a calcium nitrate aqueous solution that requires disposal, or a nitrate-based solution such as a calcium nitrate aqueous solution produced as a by-product during wet denitration treatment.

ボイラ、燃焼炉などの工業窯炉から排出される排ガス中
には、窒素酸化物(以下、NOx という)が数百PP
m含まれており、このNOxはきわめて有害であるので
排ガスから除去しなげればならない。
Exhaust gas emitted from industrial furnaces such as boilers and combustion furnaces contains several hundred PP of nitrogen oxides (hereinafter referred to as NOx).
This NOx is extremely harmful and must be removed from the exhaust gas.

従来、排ガス中のNOxを除去する方法として、NOと
NO2とのモル比がほぼ1になるようにNOをNO2に
酸化してアルカリ吸収液に吸収させる、いわゆる等モル
法、またはNOをオゾンでNO2、N2O5に酸化して
アルカリ吸収液または亜硫酸塩吸収液に吸収させる、い
わゆるオゾン法があるが、これらの方法においては副生
成物として、硝酸塩および亜硝酸塩が生成するの分、こ
れをそのまま廃棄することはできず、肥料もしくは爆薬
類の原料として再利用するか、または無害化処理を行な
わなければならない。
Conventionally, methods for removing NOx from exhaust gas include the so-called equimolar method, in which NO is oxidized to NO2 and absorbed into an alkaline absorption liquid so that the molar ratio of NO and NO2 is approximately 1, or NO is removed using ozone. There is the so-called ozone method, which oxidizes to NO2 and N2O5 and absorbs them in an alkaline absorption liquid or sulfite absorption liquid, but these methods produce nitrates and nitrites as by-products, so they are discarded as they are. They must be reused as raw materials for fertilizers or explosives, or treated to render them harmless.

これらの場合、いずれも数%の硝酸塩廃液を濃縮・乾燥
しなげればならない。
In all of these cases, several percent of the nitrate waste liquid must be concentrated and dried.

本発明の発明者らは、硝酸塩廃液の無害化を目的として
、硝酸塩を熱分解して高濃度のNOxを発生させ、これ
を還元して窒素として無害化する方法をすでに提案して
きた。
The inventors of the present invention have already proposed a method of thermally decomposing nitrates to generate a high concentration of NOx, and reducing the NOx to make it harmless as nitrogen, with the aim of making nitrate waste liquid harmless.

この方法において、硝酸カルシウム廃液の乾燥方法とし
て噴霧乾燥を行なうと、乾燥して無水化した硝酸カルシ
ウムCa (NOs ) 20粒度が微小化されすぎて
、熱分解装置とくに直熱式ロータリキルンに試料を投入
するときに粉末の飛散が激しく、この飛散粉末が原料供
給フッドに付着・堆積して操業トラブルをしばしば惹起
する原因となっていた。
In this method, when spray drying is used as a drying method for calcium nitrate waste liquid, the particle size of the dried and anhydrous calcium nitrate Ca (NOs) becomes too small, and the sample is not transferred to a pyrolysis device, especially a direct heating rotary kiln. Powder scatters violently when charging, and this scattered powder adheres to and accumulates on the raw material supply hood, often causing operational troubles.

したがって乾燥物の多量の飛散を防止するために、乾燥
物の粒度をある程度大きくする必要がある。
Therefore, in order to prevent a large amount of dried material from scattering, it is necessary to increase the particle size of the dried material to some extent.

ここで硝酸塩溶液を乾燥させるための噴霧乾燥装置を第
1図に示す。
A spray drying apparatus for drying the nitrate solution is shown in FIG.

1はスプレードライヤーで、このスプレードライヤー1
内の上部に硝酸塩溶液投入管2に接続されたスプレーノ
ズル3が設けられる。
1 is a spray dryer, this spray dryer 1
A spray nozzle 3 connected to a nitrate solution input pipe 2 is provided at the upper part of the chamber.

スプレードライヤー1の上側部には300〜400℃の
熱風を供給するための熱風供給管4が、スプレードライ
ヤー1の下側部には150〜200℃の熱風を排出する
熱風排出管5が、スプレードライヤー1の下部には硝酸
爆粉未回収容器6が接続される。
On the upper side of the spray dryer 1, there is a hot air supply pipe 4 for supplying hot air of 300 to 400°C, and on the lower side of the spray dryer 1, there is a hot air discharge pipe 5 for discharging hot air of 150 to 200°C. A nitric acid explosive powder uncollected container 6 is connected to the lower part of the dryer 1.

熱風排出管5は下部に硝酸爆粉未回収容器7を有するサ
イクロン8に接続される。
The hot air discharge pipe 5 is connected to a cyclone 8 having a container 7 for unrecovered nitric acid explosives at its lower part.

10は排ガス出口、11は2流体スプレー(後述)用の
空気供給管である。
10 is an exhaust gas outlet, and 11 is an air supply pipe for two-fluid spray (described later).

乾燥物の粒度を大きくするためには、スプレーノズル3
から噴霧する液滴を大きくすればよいが、乾燥性が悪く
なるという不都合な点が生じる。
In order to increase the particle size of the dried material, spray nozzle 3
Although it is possible to increase the size of the droplets sprayed, there is the disadvantage that the drying properties become worse.

乾燥性をよくするには乾燥温度をより高温にするか、滞
留時間を長くすればよい。
In order to improve drying performance, the drying temperature may be increased or the residence time may be increased.

しかし高温にするには限度かあ’)400’C以上の熱
風の導入は硝酸カルシウムを分解する懸念があり、また
濃縮液のなかには等モル脱硝プロセスにおげろ未複分解
物である硝酸マグネシウムMg(NO3)2が若干混入
しており、これが400℃の熱風を導入しても分解して
しまうので、熱風の温度は350℃以下とするのが望ま
しい。
However, there is a limit to how high the temperature can be raised.) There is a concern that introducing hot air over 400'C may decompose calcium nitrate, and some concentrated liquid contains magnesium nitrate (Mg), which is an unmetathesis product, in the equimolar denitrification process. A small amount of NO3)2 is mixed in, and this decomposes even if hot air at 400°C is introduced, so it is desirable that the temperature of the hot air is 350°C or lower.

また滞留時間を長くすることは、それだけスフレ−ドラ
イヤー1の塔長を大きくすることであり、このため設備
の巨大化、燃料使用量の増加をもたらすので好ましくな
い。
Furthermore, increasing the residence time means increasing the tower length of the soufflé dryer 1, which is not preferable because it increases the size of the equipment and increases the amount of fuel used.

第1図に示す噴霧乾燥装置において、乾燥性のみを重視
す☆これば、第2図に示すような液入口12に連通した
液ノズル13と、圧縮空気人口14に連通した空気ノズ
ル15とを有する2流体ノズルを用いればよいが、この
ときには8〜60μm(平均20μm)の乾燥物を得て
おり、これでは微粉末すぎる。
In the spray drying apparatus shown in FIG. 1, if only drying performance is emphasized, the liquid nozzle 13 communicating with the liquid inlet 12 and the air nozzle 15 communicating with the compressed air port 14 as shown in FIG. A two-fluid nozzle may be used, but in this case, a dried material of 8 to 60 μm (average 20 μm) is obtained, which is too fine powder.

そこで本発明の発明者らはより低温で、かつより小型の
設備(スプレードライヤー)の噴霧乾燥装置で、粒度の
より大きい硝酸カルシウムの乾燥物を得るべく、実験、
研究を重ねた結果、少量の微小粒子の炭酸カルシウムを
濃縮液に添加して分散・懸濁したものを噴霧乾燥すると
、炭酸カルシウムが核となるため乾燥物の粒子が大きく
なることを見出した。
Therefore, the inventors of the present invention conducted experiments in order to obtain dried calcium nitrate with larger particle size using a spray dryer with a lower temperature and smaller equipment (spray dryer).
As a result of repeated research, they discovered that when a small amount of fine particles of calcium carbonate were added to a concentrated liquid and the resulting mixture was spray-dried, the particles of the dried product became larger because the calcium carbonate formed the nucleus.

すなわち本発明は硝酸塩溶液または硝酸塩を主成分とす
る溶液中に、少量の、望ましくは3重量%以下の炭酸カ
ルシウムの粉末を予め分散・懸濁させた後、これを噴霧
乾燥させることにより、粒度の大きい乾燥した無水硝酸
塩を得ることを目的とするものである。
That is, the present invention involves dispersing and suspending a small amount of calcium carbonate powder, preferably 3% by weight or less, in a nitrate solution or a solution containing nitrate as a main component, and then spray-drying the powder to adjust the particle size. The purpose is to obtain a large amount of dry anhydrous nitrate.

このとき炭酸カルシウムを硝酸塩、たとえば硝酸カルシ
ウムに少量混入しても、下記の熱分解反応式を考慮する
と、炭酸カルシウムの混入は何等障害にはならない。
At this time, even if a small amount of calcium carbonate is mixed into a nitrate, such as calcium nitrate, if the following thermal decomposition reaction formula is taken into consideration, the mixing of calcium carbonate will not cause any problem.

すなわち硝酸カルシウムの熱分解を行なう場合、その熱
分解生成物である生石灰CaOの炭酸ガス化を防止する
ため、炭酸カルシウムの熱分解温度である900℃近辺
で焼成を行なうため、混入した炭酸カルシウムは熱分解
して生石灰CaOに変化してしまうからである。
In other words, when pyrolyzing calcium nitrate, in order to prevent the pyrolysis product, quicklime CaO, from turning into carbon dioxide, the calcination is carried out at around 900°C, which is the pyrolysis temperature of calcium carbonate, so the mixed calcium carbonate is This is because it thermally decomposes and changes into quicklime CaO.

つぎに本発明の実施例および比較例を示す。Next, Examples and Comparative Examples of the present invention will be shown.

実施例 硝酸カルシウム濃度20%の濃縮液(比重15/4℃1
.164)に、2重量%の炭酸カルシウムの微粒子粉末
を分散・懸濁させたものを、第1図に示す噴霧乾燥装置
を用いて22時間連続して噴霧乾燥させた。
Example Concentrated solution with calcium nitrate concentration 20% (specific gravity 15/4℃1
.. 164) with 2% by weight of calcium carbonate fine particles dispersed and suspended therein and spray-dried continuously for 22 hours using the spray-drying apparatus shown in FIG.

運転条件としては、スプレードライヤー人口の熱風温度
400℃、スプレードライヤー出口の熱風温度200℃
、濃縮液の処理量401/I(,2流体ノズル(第2図
参照)からの圧縮空気供給量11 ol/MIN、であ
った。
The operating conditions are a hot air temperature of 400℃ at the spray dryer, and a hot air temperature of 200℃ at the outlet of the spray dryer.
, the throughput of concentrated liquid was 401/I (the amount of compressed air supplied from the two-fluid nozzle (see Figure 2) was 11 ol/MIN).

この結果、硝酸カルシウムの回収率98%(硝酸爆粉未
回収容器6および7による回収率を加えた値)、乾燥硝
酸カルシウムの水分率2.3%(乾燥物を恒量になるま
で200℃で熱処理を繰り返して求めた。
As a result, the recovery rate of calcium nitrate was 98% (value including the recovery rate from containers 6 and 7 where nitric acid bomb powder was not recovered), and the moisture content of dried calcium nitrate was 2.3% (the dried material was heated at 200°C until it reached a constant weight). It was determined by repeating heat treatment.

)、粒度平均110μm(光透過式粒度分布測定法によ
り測定した。
), particle size average 110 μm (measured by light transmission particle size distribution measuring method).

)という良好な結果を得た。) good results were obtained.

比較例 実施例に用いた濃縮液と同じ濃縮液を、炭酸カルシウム
を添加・分散させることなく、実施例に用いた噴霧乾燥
装置を用いて20時間連続運転した。
Comparative Example The same concentrate as that used in the example was continuously operated for 20 hours using the spray drying apparatus used in the example without adding or dispersing calcium carbonate.

結果は硝酸カルシウムの回収率86.2%(硝酸爆粉未
回収容器6および7による回収率を加えた値)、乾燥硝
酸カルシウムの水分率3,0%(乾燥物を恒量になるま
で200℃で熱処理を繰り返して求めた。
The results showed that the recovery rate of calcium nitrate was 86.2% (adding the recovery rate from containers 6 and 7 where nitric acid bomb powder was not collected), and the moisture content of dried calcium nitrate was 3.0% (the dry matter was heated at 200°C until it reached a constant weight). It was determined by repeating the heat treatment.

)粒度平均30μrrL(光透過式粒度分布測定法によ
り測定した。
) Particle size average 30 μrrL (measured by light transmission particle size distribution measuring method).

)で、粒度が小さくしたがって回収率が悪くなっていた
), the particle size was small and the recovery rate was poor.

なお光透過式粒度分布測定法で測定した粒度分布図を第
3図に示した。
A particle size distribution diagram measured by a light transmission particle size distribution measuring method is shown in FIG.

以上説明したように、本発明は硝酸塩溶液または硝酸塩
を主成分とする溶液から、粒度の太きい乾燥した無水硝
酸塩を高回収率で得ることができるという効果を有して
いる。
As explained above, the present invention has the effect that dry anhydrous nitrate with large particle size can be obtained at a high recovery rate from a nitrate solution or a solution containing nitrate as a main component.

【図面の簡単な説明】[Brief explanation of the drawing]

第1図は本発明の実施例および比較例に用いた噴霧乾燥
装置のフローシート、第2図は2流体ノズルの断面説明
図、第3図は乾燥硝酸カルシウムの粒度分布図である。 1・・・・・・スプレードライヤー、2・・・・・・硝
酸塩溶液投入管、3・・・・・・スプレーノズル、4・
・・・・・熱風供給管、5・・・・・・熱風排出管、6
,7・・・・・・硝酸爆粉未回収容器、8・・・・・・
サイクロン、10・・・・・・排ガス出口、11・・・
・・・空気供給管、12・・・・・・液入口、13・・
・・・・液ノズル、14°°°°°゛圧縮空気入口、1
5・・・・・・空気ノズル。
FIG. 1 is a flow sheet of a spray drying apparatus used in Examples and Comparative Examples of the present invention, FIG. 2 is a cross-sectional explanatory diagram of a two-fluid nozzle, and FIG. 3 is a particle size distribution diagram of dried calcium nitrate. 1... Spray dryer, 2... Nitrate solution input tube, 3... Spray nozzle, 4...
... Hot air supply pipe, 5 ... Hot air discharge pipe, 6
, 7... Nitric acid explosive powder uncollected container, 8...
Cyclone, 10... Exhaust gas outlet, 11...
...Air supply pipe, 12...Liquid inlet, 13...
...Liquid nozzle, 14°°°°°゛Compressed air inlet, 1
5...Air nozzle.

Claims (1)

【特許請求の範囲】[Claims] 1 硝酸塩溶液または硝酸塩を主成分とする溶液中に、
少量の炭酸カルシウムの粉末を予め分散・懸濁させた後
、噴霧乾燥を行なって粒度の太きい乾燥した無水硝酸塩
を得ることを特徴とする硝酸塩溶液の乾燥方法。
1 In a nitrate solution or a solution containing nitrate as the main component,
A method for drying a nitrate solution, which comprises dispersing and suspending a small amount of calcium carbonate powder in advance, and then performing spray drying to obtain dried anhydrous nitrate having a large particle size.
JP9996476A 1976-08-20 1976-08-20 How to dry nitrate solution Expired JPS5850785B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP9996476A JPS5850785B2 (en) 1976-08-20 1976-08-20 How to dry nitrate solution

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP9996476A JPS5850785B2 (en) 1976-08-20 1976-08-20 How to dry nitrate solution

Publications (2)

Publication Number Publication Date
JPS5325266A JPS5325266A (en) 1978-03-08
JPS5850785B2 true JPS5850785B2 (en) 1983-11-12

Family

ID=14261349

Family Applications (1)

Application Number Title Priority Date Filing Date
JP9996476A Expired JPS5850785B2 (en) 1976-08-20 1976-08-20 How to dry nitrate solution

Country Status (1)

Country Link
JP (1) JPS5850785B2 (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0279597A (en) * 1988-09-14 1990-03-20 Matsushita Electric Ind Co Ltd On-vechicle speaker equipment
NO20140795A1 (en) * 2014-06-23 2015-12-24 Yara Int Asa PROCEDURE FOR THE PREPARATION OF ANNUAL CALCIUM NITRATE POWDER

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP1917213A1 (en) * 2005-07-27 2008-05-07 Alastair James Forsyth Nitrates

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0279597A (en) * 1988-09-14 1990-03-20 Matsushita Electric Ind Co Ltd On-vechicle speaker equipment
NO20140795A1 (en) * 2014-06-23 2015-12-24 Yara Int Asa PROCEDURE FOR THE PREPARATION OF ANNUAL CALCIUM NITRATE POWDER
US9908787B2 (en) 2014-06-23 2018-03-06 Yara International Asa Method for producing anhydrous calcium nitrate powder

Also Published As

Publication number Publication date
JPS5325266A (en) 1978-03-08

Similar Documents

Publication Publication Date Title
US5171552A (en) Dry processes for treating combustion exhaust gas
CA2284292C (en) Methods for the production of ammonia from urea and uses thereof
CN103785263B (en) A kind of method that ammonia vent gas treatment reclaims
US3929968A (en) Dry collection of waste materials
CN105477995A (en) Method for removing sulfur trioxide from coal-fired flue gas
CN106823717B (en) A kind of coke oven flue gas comprehensive treatment system
US4267155A (en) Process for cleaning flue gas
CN107321149A (en) Low-temp desulfurization denitrating system in coking of coal
JPH03101812A (en) Method for dry-purifying waste gas
JP4828674B2 (en) Method for producing powdered heterogeneous material
GB2232972A (en) Removing nitrogen oxides and sulphur oxides from exhaust gas
HU202422B (en) Method for removing gaseous sulfur compounds from flue gas of boilers
US4971777A (en) Process for the removal of acid components and nitrogen oxides from the waste gases of industrial furnaces
US3475121A (en) Process for absorbing so2 from gases with alkaline earth metal oxides
JPS6136969B2 (en)
JPS5850785B2 (en) How to dry nitrate solution
US20040208809A1 (en) Method of removing SO3 from flue gases
CN107398155A (en) Low-temp desulfurization denitrating system in a kind of coking of coal
JPH0359303A (en) Method for simultaneous desulfurization and denitration in furnace
JPH07308547A (en) Method of removing nitrogen oxide from waste gas
JPS61157328A (en) Purification of exhaust gas by dry dolomite method
JPS6340129B2 (en)
HU202423B (en) Method for removing gaseous sulfur compounds from flue gas of boilers
CN110986053A (en) Method for treating high-halogen hazardous waste
CN113117493A (en) Method for flue gas desulfurization and denitration by using mixed reducing agent