JPS6013964B2 - Recovery of boron compounds in flue gas desulfurization - Google Patents
Recovery of boron compounds in flue gas desulfurizationInfo
- Publication number
- JPS6013964B2 JPS6013964B2 JP56027457A JP2745781A JPS6013964B2 JP S6013964 B2 JPS6013964 B2 JP S6013964B2 JP 56027457 A JP56027457 A JP 56027457A JP 2745781 A JP2745781 A JP 2745781A JP S6013964 B2 JPS6013964 B2 JP S6013964B2
- Authority
- JP
- Japan
- Prior art keywords
- flue gas
- liquid
- gas desulfurization
- boron
- boron compounds
- 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
Links
- 150000001639 boron compounds Chemical class 0.000 title claims description 30
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 title claims description 20
- 239000003546 flue gas Substances 0.000 title claims description 20
- 238000006477 desulfuration reaction Methods 0.000 title claims description 14
- 230000023556 desulfurization Effects 0.000 title claims description 14
- 238000011084 recovery Methods 0.000 title description 3
- 239000007788 liquid Substances 0.000 claims description 33
- 239000007789 gas Substances 0.000 claims description 24
- 239000007921 spray Substances 0.000 claims description 19
- 238000010521 absorption reaction Methods 0.000 claims description 16
- 238000000034 method Methods 0.000 claims description 15
- ODINCKMPIJJUCX-UHFFFAOYSA-N Calcium oxide Chemical compound [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 claims description 14
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 claims description 11
- 239000000920 calcium hydroxide Substances 0.000 claims description 11
- 235000011116 calcium hydroxide Nutrition 0.000 claims description 11
- 229910001861 calcium hydroxide Inorganic materials 0.000 claims description 11
- 239000010440 gypsum Substances 0.000 claims description 10
- 229910052602 gypsum Inorganic materials 0.000 claims description 10
- 239000007787 solid Substances 0.000 claims description 10
- 239000000292 calcium oxide Substances 0.000 claims description 7
- 235000012255 calcium oxide Nutrition 0.000 claims description 7
- 239000002699 waste material Substances 0.000 claims description 6
- 239000007800 oxidant agent Substances 0.000 claims description 4
- 238000001694 spray drying Methods 0.000 claims description 4
- 238000001816 cooling Methods 0.000 claims description 3
- 239000011508 lime plaster Substances 0.000 claims description 2
- 239000000706 filtrate Substances 0.000 claims 2
- 239000004327 boric acid Substances 0.000 description 23
- KGBXLFKZBHKPEV-UHFFFAOYSA-N boric acid Chemical compound OB(O)O KGBXLFKZBHKPEV-UHFFFAOYSA-N 0.000 description 22
- ZOXJGFHDIHLPTG-UHFFFAOYSA-N Boron Chemical compound [B] ZOXJGFHDIHLPTG-UHFFFAOYSA-N 0.000 description 11
- 229910052796 boron Inorganic materials 0.000 description 11
- 238000000859 sublimation Methods 0.000 description 10
- 230000008022 sublimation Effects 0.000 description 10
- 238000001035 drying Methods 0.000 description 8
- 239000011521 glass Substances 0.000 description 8
- 239000002002 slurry Substances 0.000 description 7
- 239000002351 wastewater Substances 0.000 description 7
- 239000000243 solution Substances 0.000 description 6
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 6
- 239000000463 material Substances 0.000 description 5
- 239000002245 particle Substances 0.000 description 5
- 235000008733 Citrus aurantifolia Nutrition 0.000 description 4
- 235000011941 Tilia x europaea Nutrition 0.000 description 4
- 239000004571 lime Substances 0.000 description 4
- 239000003595 mist Substances 0.000 description 4
- 239000000428 dust Substances 0.000 description 3
- 238000004519 manufacturing process Methods 0.000 description 3
- 239000002994 raw material Substances 0.000 description 3
- VTYYLEPIZMXCLO-UHFFFAOYSA-L Calcium carbonate Chemical compound [Ca+2].[O-]C([O-])=O VTYYLEPIZMXCLO-UHFFFAOYSA-L 0.000 description 2
- 244000025254 Cannabis sativa Species 0.000 description 2
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 2
- GBAOBIBJACZTNA-UHFFFAOYSA-L calcium sulfite Chemical compound [Ca+2].[O-]S([O-])=O GBAOBIBJACZTNA-UHFFFAOYSA-L 0.000 description 2
- 235000010261 calcium sulphite Nutrition 0.000 description 2
- 239000013078 crystal Substances 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 239000012530 fluid Substances 0.000 description 2
- 239000000047 product Substances 0.000 description 2
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 1
- 241000282693 Cercopithecidae Species 0.000 description 1
- 235000001543 Corylus americana Nutrition 0.000 description 1
- 240000007582 Corylus avellana Species 0.000 description 1
- 235000007466 Corylus avellana Nutrition 0.000 description 1
- 235000008597 Diospyros kaki Nutrition 0.000 description 1
- 244000236655 Diospyros kaki Species 0.000 description 1
- FYYHWMGAXLPEAU-UHFFFAOYSA-N Magnesium Chemical compound [Mg] FYYHWMGAXLPEAU-UHFFFAOYSA-N 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 239000007864 aqueous solution Substances 0.000 description 1
- 229910052788 barium Inorganic materials 0.000 description 1
- DSAJWYNOEDNPEQ-UHFFFAOYSA-N barium atom Chemical compound [Ba] DSAJWYNOEDNPEQ-UHFFFAOYSA-N 0.000 description 1
- 229910052791 calcium Inorganic materials 0.000 description 1
- 239000011575 calcium Substances 0.000 description 1
- 229910000019 calcium carbonate Inorganic materials 0.000 description 1
- 239000004106 carminic acid Substances 0.000 description 1
- DGQLVPJVXFOQEV-NGOCYOHBSA-N carminic acid Chemical compound OC1=C2C(=O)C=3C(C)=C(C(O)=O)C(O)=CC=3C(=O)C2=C(O)C(O)=C1[C@H]1O[C@H](CO)[C@@H](O)[C@H](O)[C@H]1O DGQLVPJVXFOQEV-NGOCYOHBSA-N 0.000 description 1
- 229940114118 carminic acid Drugs 0.000 description 1
- 235000012730 carminic acid Nutrition 0.000 description 1
- 239000000460 chlorine Substances 0.000 description 1
- 229910052801 chlorine Inorganic materials 0.000 description 1
- -1 chlorine ions Chemical class 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 239000000446 fuel Substances 0.000 description 1
- 239000000295 fuel oil Substances 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 239000008235 industrial water Substances 0.000 description 1
- 238000011005 laboratory method Methods 0.000 description 1
- 229910052749 magnesium Inorganic materials 0.000 description 1
- 239000011777 magnesium Substances 0.000 description 1
- 229910052943 magnesium sulfate Inorganic materials 0.000 description 1
- 239000002244 precipitate Substances 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
- 238000002798 spectrophotometry method Methods 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
Landscapes
- Treating Waste Gases (AREA)
- Removal Of Specific Substances (AREA)
Description
【発明の詳細な説明】
本発明は溢式排煙脱硫法排液中のホウ素化合物の回収に
関し、より詳しくはガラス工場などの排ガス中に含まれ
るホウ素化合物を溢式石灰石膏法排煙脱硫の排液から回
収する方法及びその装直に関する。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to the recovery of boron compounds in the effluent of the overflow flue gas desulfurization method, and more specifically, the present invention relates to the recovery of boron compounds contained in the flue gas of glass factories, etc., by the overflow lime plaster method flue gas desulfurization method. This invention relates to a method of recovering liquid from wastewater and its reloading.
ガラス工場の排ガス中にはガス状又は固体形機でホウ素
化合物が飛散してくる場合がある。Boron compounds may be dispersed into the exhaust gas from glass factories by gaseous or solid machines.
このような排ガスを湿式排煙脱硫処理すると吸収塔で除
去されたホウ素化合物が吸収液中に溶け込み排液中に含
まれて系外に排出される。徴量のホウ素は嬢作物に対す
る必要な元素であるが多量のホウ素化合物を含む排液は
農作物に対し有害であり、そのようなホウ素含有擬液か
らホウ素を除去することが必要である。しかし現在排液
からホウ素を除く特に実用化された方法がなく、僅かに
実験室的方法としてホゥ酒石酸バリウム法により沈殿と
して分離する方法が知られているにすぎない。またホウ
素化合物は資源的に不足する煩向にあるのでその回収が
望ましい。排水からのホウ素の分離は困難であり、上記
湿式排ガス処理系において系の無排水化を図り排ガスの
磯熱を利用して排水を噂霧乾燥しホウ素化合物を回収す
ることを考えたがしかし&03,HB02.はBQなど
のホウ素化合物は水蒸気を含んだガス中で著しく揮発性
で排水を蜂務乾燥しても含有ホウ素化合物が昇華して固
体として回収されないことが顔らかになった。When such exhaust gas is subjected to wet flue gas desulfurization treatment, the boron compounds removed in the absorption tower are dissolved in the absorption liquid, contained in the waste liquid, and discharged outside the system. Boron is a necessary element for crops, but wastewater containing large amounts of boron compounds is harmful to crops, and it is necessary to remove boron from such boron-containing simulated solutions. However, there is currently no practical method for removing boron from wastewater, and the only known laboratory method is to separate it as a precipitate using the barium borotartrate method. In addition, since boron compounds are in short supply as a resource, it is desirable to recover them. It is difficult to separate boron from wastewater, and we have considered making the system wastewater-free in the wet exhaust gas treatment system mentioned above and using the heat of the ocean to dry the wastewater and recover the boron compounds, but... , HB02. It has become clear that boron compounds such as BQ are extremely volatile in gases containing water vapor, and even when wastewater is dried, the boron compounds sublimed and cannot be recovered as solids.
しかるに排水にある蟹物質を添加することにより上記燈
霧乾燥中のホウ素化合物の昇華を抑制し、粒径の大きい
頃鞍乾燥を生じてサイクロン等による捕集を容易にし、
しかも回収物をガラス製造原料として再利用できること
が見出された。However, by adding crab substances to the wastewater, the sublimation of the boron compounds during the light mist drying is suppressed, and when the particle size is large, saddle drying occurs, making it easier to collect with a cyclone, etc.
Moreover, it was discovered that the recovered material could be reused as a raw material for glass production.
本発明はガラス工場等の排ガス中に含まれるホウ素を湿
式石灰石膏法排煙脱硫排液から回収することを目的とす
る。また本発明は排ガス中のホウ素をガラス製造原料と
して再利用可能な形態で回収することを目的とし、さら
に本発明は湿式石灰石膏法排煙脱硫装置の無排液化を図
ることを目的とする。本発明の方法は湿式排煙脱硫の系
外排出液に消石灰又は生石灰を添加し、これを脱硫処理
すべき高温排ガスを熱源として噂霧乾燥しホウ素化合物
を固体として回収する方法であり、それにより排煙脱硫
装置の系外排出液の糠鱗液化を図ることができる。The object of the present invention is to recover boron contained in flue gas from a glass factory or the like from a wet lime-gypsum process flue gas desulfurization effluent. Another object of the present invention is to recover boron in flue gas in a form that can be reused as a raw material for glass production, and a further object of the present invention is to make a wet lime gypsum flue gas desulfurization device liquid-free. The method of the present invention is a method in which slaked lime or quicklime is added to the liquid discharged from the system during wet flue gas desulfurization, and this is fog-dried using the high-temperature flue gas to be desulfurized as a heat source to recover boron compounds as solids. It is possible to liquefy the liquid discharged from the flue gas desulfurization system into bran scales.
本発明の装置は緑式石灰石膏法排煙脱硫装置に渡液調整
装鷹を設遣し、排ガス贋霧冷却装置を前記調整猿液の噴
霧乾燥を可能にした装置である。以下第1図を参照して
本発明を説明する。The apparatus of the present invention is a green lime gypsum method flue gas desulfurization apparatus equipped with a liquid passing adjustment device, and a flue gas mist cooling device that enables spray drying of the adjusted liquid. The present invention will be explained below with reference to FIG.
処理すべき排ガス1はスプレードライヤー2で増緑冷却
される。スプレードライヤー2には後記調整鱗液が靖綾
され排ガスーは排液の乾嬢熱源となり鱗液により増溢冷
却され、排液は贋霧乾燥され固体となる。排ガスはサイ
クロン3を通過後煙道内で水スプレーされてさらに増緑
冷却され吸収塔4に入り循環吸収液に接触してS0x、
ダスト、ホウ素化合物を吸収液中に除去されデミスター
5を経て清浄ガスとして排出される。吸収液に吸収され
たS0xは液中の消石灰、炭酸カルシウムと反応して亜
硫酸カルシウム又は石膏となり吸収されたホウ素化合物
は水綾性ホウ酸塩となる。吸収塔循環液の一部は液面制
御によって抜出され酸化器6へ送られる。そこで硫酸を
添加して未反応カルシウムを処理するとともに含まれる
亜硫酸カルシウムを空気酸化して石膏に転化する。酸化
器6から抜出されたスラリーは貯槽7を経て分離器8に
おいて石膏9と櫨液に分離される。ホウ素化合物は水溶
性のために猿液側に移り、渡液は調整槽10‘こ1時貯
留される。貯留の間に瀦液に消石灰又は生石灰を添加し
糠液をアルカリ性解にする。調整後の櫨液はスラリーと
してスプレードライヤー2に頃霧される。噴落されたス
ラリーはスプレードライヤー2中で、前記のように高温
排ガスの頭熱により蒸発乾固してスプレ−ドライヤーの
底又はサイクロン3からホウ素化合物を含む固体として
回収される。調整槽101こ添加される梢石灰又は生石
灰は調整後のスラリーがスプレードライヤーにおいてス
プレーできる粒径のスラリーを生ずれば良く、200メ
ッシュ以下の粒径のもので良好に操作できた。添加量は
調整後のスラリーのPHを7.5以上とする量で十分で
あり、ホウ素化合物1モルに対して0.5〜1モル程度
が適当であった。消石灰又は生石灰を添加調整したスラ
リーはスプレードライヤーにおける頃霧乾燥時のホウ素
化合物の昇華を抑え、また消石灰の不溶解粒子が核とな
り粒径の大きい乾燥物を生じてスプレ−ドライヤ−の収
率を上昇させる。前記プロセスにおいて分離器8の櫨液
に消石灰を添加することなく噂務乾燥すると乾燥時にホ
ウ素化合物は昇華して再び吸収塔内に入り、そこで吸収
液に捕捉される。The exhaust gas 1 to be treated is cooled and greened by a spray dryer 2. The spray dryer 2 is supplied with the adjusted scale liquid, which will be described later, and the exhaust gas serves as a heat source for drying the waste liquid, which is flooded and cooled by the scale liquid, and the waste liquid is dried and solidified. After passing through the cyclone 3, the exhaust gas is sprayed with water in the flue to further green and cool, enters the absorption tower 4, comes into contact with the circulating absorption liquid, and becomes S0x,
Dust and boron compounds are removed from the absorption liquid, which is then discharged as clean gas through the demister 5. The SOx absorbed in the absorption liquid reacts with slaked lime and calcium carbonate in the liquid to become calcium sulfite or gypsum, and the absorbed boron compound becomes hydroborate. A part of the absorption tower circulating liquid is extracted by liquid level control and sent to the oxidizer 6. Therefore, sulfuric acid is added to treat unreacted calcium, and the calcium sulfite contained therein is oxidized in the air and converted into gypsum. The slurry extracted from the oxidizer 6 passes through a storage tank 7 and is separated into gypsum 9 and oak liquor in a separator 8. Since the boron compound is water-soluble, it moves to the monkey fluid side, and the passed fluid is temporarily stored in the adjustment tank 10'. During storage, slaked lime or quicklime is added to the bran to make it alkaline. The adjusted hazel liquor is atomized into a spray dryer 2 as a slurry. The sprayed slurry is evaporated to dryness in the spray dryer 2 by the head heat of the high-temperature exhaust gas as described above, and is recovered from the bottom of the spray dryer or the cyclone 3 as a solid containing boron compounds. The canopy lime or quicklime added to the adjustment tank 101 is sufficient as long as the slurry after adjustment produces a slurry with a particle size that can be sprayed in a spray dryer, and it was possible to operate satisfactorily with a particle size of 200 mesh or less. The amount added was sufficient to make the pH of the slurry after adjustment 7.5 or more, and the appropriate amount was about 0.5 to 1 mol per 1 mol of the boron compound. Slurry prepared by adding slaked lime or quicklime suppresses the sublimation of boron compounds during mist drying in a spray dryer, and the undissolved particles of slaked lime act as cores to form a dried product with a large particle size, increasing the yield of the spray dryer. raise. In the above process, if the oak liquor in the separator 8 is dried without adding slaked lime, the boron compound sublimes during drying and enters the absorption tower again, where it is captured by the absorption liquid.
従ってホウ素化合物は分離器8において分離される石膏
の付着水に伴なわれるものを除き系外に排出されないの
で、吸収液中のホウ素化合物の濃度が次第に上昇し、濠
液を系外に排出することが必要になる。本発明によれば
石膏分離後の渡液をスプレードライヤーに循環して贋霧
乾燥してホウ素化合物を回収し、系を無鱗液化し、しか
し回収したホウ素化合物をガラス製造原料として利用で
きる。Therefore, boron compounds are not discharged out of the system except for those accompanied by the water adhering to the gypsum separated in the separator 8, so the concentration of boron compounds in the absorption liquid gradually increases and the moat liquid is discharged out of the system. It becomes necessary. According to the present invention, the transferred liquid after gypsum separation is circulated to a spray dryer, and the boron compound is recovered by mist drying, the system is rendered scale-free, and the recovered boron compound can be used as a raw material for glass production.
試験例ホウ素化合物の昇華試験
第2図に示す菱直を用いてホウ素化合物の昇華試験を行
なった。Test Example Sublimation Test of Boron Compounds A sublimation test of boron compounds was conducted using a rhombus tube shown in FIG.
垣温糟1 1で65℃に保った水を容れた吸収ピン12
にN280%、0210%、C0210%のドライガス
を3そ/分の速度で通して水分20%程度に加湿し、水
分が凝縮しないように保温して環状炉13に通す。環状
炉13には試料約2夕を入れたボート14が鷹かれ15
0〜250℃の範囲内の一定温度に保たれる。環状炉1
3を通ったガスはN/1皿aOH水溶液を容れた吸収ビ
ン15に進み随伴されたホウ素化合物を吸収させる。吸
収液はカルミン酸を用いて吸光光度法によりホウ酸量を
測定し、通したガス量はガスメーター16で記録した。
ホワ酸結晶、ガラス工場採取ダスト(分析値よりほとん
どホウ酸と考えられる)及びホウ酸水に消石灰を等モル
添加し乾燥した乾固物について行った結果は第3図に示
される。Absorption pin 12 containing water kept at 65℃ at Kaki Onsu 1 1
A dry gas of 80% N2, 10% CO2, and 10% C02 is passed through it at a rate of 3 sops/min to humidify the material to about 20% moisture, and the material is kept warm so that the water does not condense and passed through the annular furnace 13. A boat 14 containing about 2 samples was loaded into the annular furnace 13.
The temperature is maintained at a constant temperature within the range of 0 to 250°C. Annular furnace 1
The gas that has passed through 3 advances to an absorption bottle 15 containing N/1 dish of aOH aqueous solution and absorbs the accompanying boron compound. The amount of boric acid was measured by spectrophotometry using carminic acid as the absorption liquid, and the amount of gas passed was recorded with a gas meter 16.
The results are shown in FIG. 3 for boric acid crystals, dust collected from a glass factory (which is thought to be mostly boric acid based on the analytical values), and a dried product obtained by adding equimolar amounts of slaked lime to boric acid water.
ホウ酸結晶、ガラス工場採取ダストは何れも水分を含む
ガス中で著しい昇華性を示し、消石灰添加試料の昇華性
は著しく抑制されることが明らかである。実施例
排煙脱硫想定擬液にホゥ酸を1〜2%加えたホウ素含有
液及び前記ホウ素含有液に消石灰をホウ素1モルに対し
0.7モル添加した液を頃菱乾燥した。It is clear that both boric acid crystals and glass factory dust exhibit remarkable sublimation in gas containing moisture, and that the sublimation of the slaked lime-added sample is significantly suppressed. Example A boron-containing solution prepared by adding 1 to 2% boric acid to a simulated flue gas desulfurization solution, and a solution obtained by adding 0.7 mole of slaked lime per mole of boron to the boron-containing solution were dried.
乾燥室直径約200仇舷◇のスプレードライヤーを用い
アトマィザーは約800比pmで回転させた。A spray dryer with a drying chamber diameter of about 200 m² was used, and the atomizer was rotated at about 800 pm.
スプレードライヤーの熱源にはA重油を燃料として熱風
発生炉で約80ぴ0の高温ガスを発生させ空気で稀釈し
て200〜300℃としたガスを用いた。乾燥できる液
量は30夕/時で、ガス草は約10側め/時である。乾
燥物は排ガスとともにサイクロンに入りそこで俺集され
る。排煙脱硫の排液はホウ酸の他に石膏、工水中の塩素
イオン、石灰の不純物としてマグネシウムが含有される
と考えられるのでホウ酸約2%の水溶液にCaC12,
MgS04を添加した下記成分を有する液を想定擬液と
して用いた。As the heat source of the spray dryer, a high-temperature gas of about 80 psi was generated in a hot air generator using A heavy oil as fuel, and the gas was diluted with air to a temperature of 200 to 300°C. The amount of liquid that can be dried is 30 evenings/hour, and gas grass can be dried at about 10 evenings/hour. The dried materials enter the cyclone together with the exhaust gas, where they are collected. In addition to boric acid, the effluent from flue gas desulfurization is thought to contain gypsum, chlorine ions in the industrial water, and magnesium as impurities from lime.
A liquid containing MgS04 and having the following components was used as a simulated liquid.
比BQI9.5 (夕/々) Ca2十0.007 (m。ratio BQI9.5 (evening/split) Ca20.007 (m.
1ノク)
* Sの‐0.02 (mol/そ)
CIIO○ (mg/そ)PH
52試験において下記4点を測定しホウ酸の物質収支
を計算した。1 noku) * S-0.02 (mol/so) CIIO○ (mg/so) PH
In the 52 test, the following four points were measured and the material balance of boric acid was calculated.
{1’スプレードライヤーで処理したホウ酸量:処理液
量、液中のホウ酸濃度より算出、‘21 補集ホウ酸量
:補集蒸発乾固物量と固形分中のホウ酸濃度より算出、
‘31 昇華ホゥ酸草:排ガス量、排ガス中のガス体ホ
ゥ酸濃度(吸収ビンを用いN/1側aOH水溶液で橘集
)より算出、‘4’飛散固体ホウ酸量(サイクロンで補
集されない固体ホゥ酸童)排ガス量、排ガス中のダスト
濃度、ダスト中のホウ酸濃度より算出、結果は表1に示
す。{1' Amount of boric acid treated with a spray dryer: Calculated from the amount of treated liquid and boric acid concentration in the liquid, '21 Amount of collected boric acid: Calculated from the collected amount of evaporated solids and boric acid concentration in the solid content,
'31 Sublimated boric acid grass: Calculated from exhaust gas amount, gaseous boric acid concentration in exhaust gas (collected with aqueous aOH solution on the N/1 side using an absorption bottle), '4' amount of scattered solid boric acid (not collected by cyclone) The results are shown in Table 1. The results are shown in Table 1.
表 一 1 スプレードラィャ−の噴霧乾燥試験
注:村酸補集率=鷺側o
村酸昇華率=俄・oo
固体ホウ酸飛散率こ篭X・oo
ホゥ酸構築率十ホウ酸昇華率+固体ホウ酸飛散率の合計
が100%にならず8〜90%であるがスプレードライ
ヤーの内壁に付着したホウ酸もあると考えられるのでこ
の値は妥当な値である。Table 1 1 Spray drying test of spray dryer Note: Murata collection rate = Sagi side o Murata sublimation rate = 迄・oo Solid boric acid scattering rate Koko X・oo Boric acid construction rate Deca boric acid sublimation rate + solid boric acid Although the total acid scattering rate is not 100% but 8 to 90%, this value is a reasonable value since it is thought that some boric acid adhered to the inner wall of the spray dryer.
表1からホウ素含有排液そのま)のスプレ−ドライヤー
贋髪乾燥ではホゥ酸橋集率が1%で、ほとんどが昇華し
てガス体となり飛散するが、消石灰添加排液ではホウ酸
補集率は70%に達し、ホゥ酸昇華率もかな.り低く抑
制されることが明らかである。From Table 1, when drying fake hair with a spray dryer using a boron-containing waste liquid (as is), the boric acid bridge collection rate is 1%, and most of it sublimates and becomes a gas and scatters, but in the case of slaked lime-added waste liquid, the boric acid collection rate is 1%. reaches 70%, and the boric acid sublimation rate is also high. It is clear that the reduction is suppressed to a low level.
第1図は本発明の装置の工程説明図、第2図はホウ素化
合物昇華試験装置の説明図、第3図はホウ素化合物昇華
性を示すグラフである。
1…・・・排ガス、2・・・・・・スプレードライヤー
、4・・・・・・吸収塔、6・・・・・・酸化器、8・
・…・分離器、10・・・・・・調整槽。
第1図
第2図
第3図FIG. 1 is an explanatory diagram of the process of the apparatus of the present invention, FIG. 2 is an explanatory diagram of the boron compound sublimation test apparatus, and FIG. 3 is a graph showing the sublimability of boron compounds. 1... Exhaust gas, 2... Spray dryer, 4... Absorption tower, 6... Oxidizer, 8...
...Separator, 10...Adjustment tank. Figure 1 Figure 2 Figure 3
Claims (1)
液に消石灰又は生石灰を添加して噴霧乾燥しホウ素化合
物を固体として回収する方法。 2 消石灰又は生石灰を添加した排出液の噴霧乾燥の熱
源に脱硫処理すべき高温排ガスを使用し前記排ガスを増
湿冷却し系を無排液化する特許請求の範囲第1項記載の
方法。 3 排ガス噴霧冷却装置、吸収塔、酸化器、分離器を含
む湿式石灰石膏法排煙脱硫装置において、分離器からの
排液に消石灰又は生石灰を添加しpHを調整する濾液調
整装置を設置し、前記噴霧冷却装置を前記調整濾液の噴
霧乾燥を可能にしてなるホウ素化合物を回収し無排液化
した排煙脱硫装置。[Claims] 1. In flue gas desulfurization using the wet lime plaster method, slaked lime or quicklime is added to the liquid discharged from the system, and the boron compound is recovered as a solid by spray drying. 2. The method according to claim 1, wherein the high-temperature exhaust gas to be desulfurized is used as a heat source for spray drying the discharge liquid to which slaked lime or quicklime has been added, and the exhaust gas is humidified and cooled to make the system liquid-free. 3. In a wet lime-gypsum method flue gas desulfurization system that includes a flue gas spray cooling device, an absorption tower, an oxidizer, and a separator, a filtrate adjustment device is installed to adjust the pH by adding slaked lime or quicklime to the waste liquid from the separator, A flue gas desulfurization device that enables the spray cooling device to spray dry the adjusted filtrate and recovers a boron compound to eliminate liquid discharge.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP56027457A JPS6013964B2 (en) | 1981-02-26 | 1981-02-26 | Recovery of boron compounds in flue gas desulfurization |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP56027457A JPS6013964B2 (en) | 1981-02-26 | 1981-02-26 | Recovery of boron compounds in flue gas desulfurization |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS57145024A JPS57145024A (en) | 1982-09-07 |
| JPS6013964B2 true JPS6013964B2 (en) | 1985-04-10 |
Family
ID=12221639
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP56027457A Expired JPS6013964B2 (en) | 1981-02-26 | 1981-02-26 | Recovery of boron compounds in flue gas desulfurization |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS6013964B2 (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US20150352490A1 (en) * | 2013-01-24 | 2015-12-10 | Mitsubishi Heavy Industries, Ltd. | Air pollution control system and air pollution control method |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| DE10323774A1 (en) * | 2003-05-26 | 2004-12-16 | Khd Humboldt Wedag Ag | Process and plant for the thermal drying of a wet ground cement raw meal |
| JP4615234B2 (en) * | 2004-03-30 | 2011-01-19 | 独立行政法人科学技術振興機構 | Method for insolubilizing and separating boron dissolved in water, method for detoxifying boron dissolved wastewater, and method for recovering boron resources |
-
1981
- 1981-02-26 JP JP56027457A patent/JPS6013964B2/en not_active Expired
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US20150352490A1 (en) * | 2013-01-24 | 2015-12-10 | Mitsubishi Heavy Industries, Ltd. | Air pollution control system and air pollution control method |
| US9669356B2 (en) * | 2013-01-24 | 2017-06-06 | Mitsubishi Heavy Industries, Ltd. | Air pollution control system and air pollution control method |
| US9943804B2 (en) | 2013-01-24 | 2018-04-17 | Mitsubishi Heavy Industries, Ltd. | Air pollution control system and air pollution control method |
Also Published As
| Publication number | Publication date |
|---|---|
| JPS57145024A (en) | 1982-09-07 |
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