JP3110251B2 - Low-grade gypsum separation and recovery method - Google Patents
Low-grade gypsum separation and recovery methodInfo
- Publication number
- JP3110251B2 JP3110251B2 JP06146141A JP14614194A JP3110251B2 JP 3110251 B2 JP3110251 B2 JP 3110251B2 JP 06146141 A JP06146141 A JP 06146141A JP 14614194 A JP14614194 A JP 14614194A JP 3110251 B2 JP3110251 B2 JP 3110251B2
- Authority
- JP
- Japan
- Prior art keywords
- gypsum
- slurry
- low
- grade
- filtration
- 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 - Fee Related
Links
Landscapes
- Treating Waste Gases (AREA)
- Filtration Of Liquid (AREA)
- Compounds Of Alkaline-Earth Elements, Aluminum Or Rare-Earth Metals (AREA)
Description
【0001】[0001]
【産業上の利用分野】本発明は湿式石灰石膏法排煙脱硫
装置で副生する石膏スラリの一部と同装置に付属する排
水処理装置から発生する汚泥スラリを混合して低品位石
膏を分離回収する方法の改良に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention separates low-grade gypsum by mixing a part of gypsum slurry produced as a by-product in a wet lime gypsum method flue gas desulfurization apparatus and sludge slurry generated from a wastewater treatment apparatus attached to the apparatus. It relates to improvement of the method of collecting.
【0002】[0002]
【従来の技術】石炭焚きボイラ排ガスの如くダストを多
量に含む排ガス中のSOxを湿式石灰石膏法排煙脱硫装
置で処理する場合には、脱硫装置からの排水を処理する
排水処理装置からフライアッシュ,CaF2 ,Al(O
H)3 ,Mg(OH)2 ,Fe(OH)3 などの汚泥成
分が発生する。この汚泥成分を埋めたてなどで処理する
場合には、その処理費が高く、またハンドリングが難し
いため、湿式石灰石膏法排煙脱硫装置で副生する石膏
(石膏純度95〜98wt%)の一部に同装置に付属す
る排水処理装置から発生する汚泥を混合して低品位石膏
(石膏純度80〜90wt%)として回収し、セメント
混合剤として有効利用することが行われている。このセ
メント混合剤としての低品位石膏の品質は引取メーカー
から、セメント材料への塩害を防止するために低品位石
膏中のCl- 濃度として100〜150mg/kg(ド
ライベース)、また含水率として20wt%以下の品質
を要求されている。2. Description of the Related Art When SOx in flue gas containing a large amount of dust, such as flue gas from a coal-fired boiler, is treated by a wet lime-gypsum method flue gas desulfurization device, fly ash is supplied from a wastewater treatment device that treats wastewater from the desulfurization device. , CaF 2 , Al (O
Sludge components such as H) 3 , Mg (OH) 2 , and Fe (OH) 3 are generated. When this sludge component is treated by burying it, the treatment cost is high and handling is difficult. Therefore, one of the gypsum (purity of gypsum: 95 to 98 wt%) produced as a by-product in the wet lime-gypsum method flue gas desulfurization apparatus is used. Sludge generated from a wastewater treatment device attached to the device is mixed in the section and collected as low-grade gypsum (purity of gypsum: 80 to 90 wt%), and is effectively used as a cement mixture. The quality of the low-grade gypsum as a cement admixture was determined by a take-off maker to prevent salt damage to the cement material by 100-150 mg / kg (dry base) as the Cl - concentration in the low-grade gypsum and 20 wt. % Or less quality is required.
【0003】従来この低品位石膏の分離回収装置として
遠心分離機が使用されていた。以下、図5により従来の
低品位石膏分離回収方法について説明する。湿式石灰石
膏法排煙脱硫装置で副生する石膏スラリ1と排水処理装
置からの汚泥スラリ2が分離機供給槽3で混合され、ポ
ンプ4で経路5を経て遠心分離機6に供給される。この
遠心分離機6は高速で運転され固体と液体とを分離し、
固体である低品位石膏は洗浄水10で洗浄しCl- 濃度
を下げた後、さらに脱水されて経路7から排出される。
回収されたケークはベルトコンベヤ8で所定の場所に移
送され低品位石膏9として回収される。一方、ろ液及び
オーバーフロー液は経路11からろ液槽12に送られ
る。このろ液槽12は数重量%のスラリを含むため、ポ
ンプ13で経路14からろ液シックナ15に送られ固体
分を沈降分離する。ろ液シックナ15の下部からの濃縮
スラリ16はポンプ17で経路18を経て分離機供給槽
3に戻される。一方、上澄液は経路19から排水槽20
に一旦溜められた後、ポンプ21で経路22を介して総
合排水処理装置へ返送される。Conventionally, a centrifugal separator has been used as a device for separating and recovering this low-grade gypsum. Hereinafter, a conventional low-grade gypsum separation and recovery method will be described with reference to FIG. A gypsum slurry 1 produced as a by-product in a wet lime-gypsum method flue gas desulfurization apparatus and a sludge slurry 2 from a wastewater treatment apparatus are mixed in a separator supply tank 3 and supplied to a centrifugal separator 6 via a path 5 by a pump 4. This centrifuge 6 is operated at high speed to separate solid and liquid,
Low-grade gypsum which is solid is washed with washing water 10 Cl - After lowering the concentration is further discharged from dehydrated by path 7.
The recovered cake is transferred to a predetermined place by a belt conveyor 8 and recovered as low-grade gypsum 9. On the other hand, the filtrate and the overflow liquid are sent from the path 11 to the filtrate tank 12. Since this filtrate tank 12 contains a slurry of several weight%, it is sent from a path 14 to a filtrate thickener 15 by a pump 13 to settle and separate solids. The concentrated slurry 16 from the lower part of the filtrate thickener 15 is returned to the separator supply tank 3 via the path 18 by the pump 17. On the other hand, the supernatant liquid flows from the drainage tank 20 through the path 19.
Is once returned to the integrated wastewater treatment device via the path 22 by the pump 21.
【0004】[0004]
【発明が解決しようとする課題】低品位石膏分離回収装
置として遠心分離機を使用する従来法においては脱水性
はよく、ケークの含水率を10wt%まで下げることも
可能であり、平均粒径が30〜50μmの副生石膏(石
膏純度95〜98wt%)を分離・回収するには有効で
あるが、平均粒径が2〜10μmのような微粒子の汚泥
スラリを含む低品位石膏を分離する際には遠心力により
ケーク層が圧密されろ過性が悪くなる。従ってスラリ給
液速度及び洗浄水供給速度も遅くする必要が生じ、所定
量のスラリを処理するためには遠心分離機の基数を増す
必要がある。また、回分式であるため、その制御も複雑
であり、メンテナンスが繁雑であると共にろ液シックナ
が必要となり設備的にもコスト高になる欠点があった。
また、ろ過性が悪いため、Cl- の洗浄に際しても効率
が悪く長時間を要する欠点があった。本発明は上記技術
水準に鑑み、設備的にも安価で、かつCl- の洗浄効率
のよい低品位石膏分離方法を提案しようとするものであ
る。In the conventional method using a centrifugal separator as a low-grade gypsum separation and recovery device, the dewatering property is good, the water content of the cake can be reduced to 10% by weight, and the average particle size can be reduced. It is effective for separating and recovering by-product gypsum of 30 to 50 μm (gypsum purity of 95 to 98 wt%). However, when separating low-grade gypsum containing fine-particle sludge slurry having an average particle size of 2 to 10 μm. In the case, the cake layer is compacted by centrifugal force and the filterability deteriorates. Therefore, it is necessary to reduce the slurry supply speed and the washing water supply speed, and it is necessary to increase the number of centrifuges in order to process a predetermined amount of slurry. In addition, since it is a batch type, the control thereof is complicated, maintenance is complicated, and a filtrate thickener is required, so that there are drawbacks in that equipment becomes expensive.
In addition, because of poor filtration properties, there is a drawback that the efficiency is low and a long time is required for cleaning Cl − . In view of the above prior art, is inexpensive to equipment specific and Cl - is intended to propose a method cleaning efficiency of good low-grade gypsum separation.
【0005】[0005]
【課題を解決するための手段】本発明は (1)湿式石灰石膏法排煙脱硫装置で副生する石膏スラ
リの一部と同装置に付属する排水処理装置から発生する
汚泥スラリとを混合して低品位石膏を分離回収する方法
において、該混合スラリを水平ベルト式真空脱水機で処
理することを特徴とする低品位石膏分離回収方法。 (2)水平ベルト式真空脱水機のベルトに予め石膏スラ
リでプレコート層を形成することを特徴とする上記
(1)記載の低品位石膏分離回収方法。 である。SUMMARY OF THE INVENTION The present invention relates to (1) mixing a part of gypsum slurry by-produced in a wet lime-gypsum method flue gas desulfurization apparatus and a sludge slurry generated from a wastewater treatment apparatus attached to the apparatus. A method for separating and recovering low-grade gypsum by treating the mixed slurry with a horizontal belt vacuum dehydrator. (2) The method for separating and recovering low-grade gypsum according to the above (1), wherein a precoat layer is previously formed on the belt of the horizontal belt type vacuum dehydrator with gypsum slurry. It is.
【0006】すなわち、本発明は従来の遠心分離機に代
えて水平ベルト式真空脱水機を採用することにより、遠
心分離機のように強い力で圧密されることもなくろ過性
も良好で、かつ連続的な分離回収が可能となり、ろ液シ
ックナが不要となるなどシンプルとなり設備的にも安価
で経済的な方法を提供するものである。さらに、水平ベ
ルト式真空脱水機の処理工程を石膏スラリでプレコート
層を形成した後、石膏スラリと汚泥スラリの混合物を供
給し処理することにより水平ベルト式真空脱水機のろ布
の目詰りもなく、長時間安定したろ過性を維持させるこ
とができる。ろ過性がよいことはCl- の洗浄効果も高
まることであり、低品位石膏中のCl- 濃度として10
0〜150mg/kg(ドライベース)また含水率も2
0wt%以下の品質が確保でき引取メーカの要求値を満
足することができる。That is, the present invention employs a horizontal belt type vacuum dehydrator in place of the conventional centrifugal separator, so that it is not compacted by a strong force unlike the centrifugal separator and has good filterability. The present invention provides a simple, simple and inexpensive and economical method in terms of equipment because continuous separation and recovery can be performed and a filtrate thickener is not required. Furthermore, the processing step of the horizontal belt type vacuum dehydrator is performed by forming a pre-coat layer with gypsum slurry, and then supplying and processing a mixture of the gypsum slurry and the sludge slurry without clogging of the filter cloth of the horizontal belt type vacuum dehydrator. , And can maintain stable filterability for a long time. It is a good filterability is Cl - is a also increases that cleaning effect, Cl low-grade gypsum - 10 as the concentration
0-150mg / kg (dry base) and water content 2
The quality of 0 wt% or less can be ensured and the demand value of the take-off maker can be satisfied.
【0007】[0007]
【作用】湿式石灰石膏法排煙脱硫装置で副生する石膏ス
ラリの濃度は約20重量%の高スラリでかつ平均粒径も
30〜50μmと大きく、このような高品位の石膏を処
理するには遠心分離機が適しているが、平均粒径が2〜
10μmのようなフライアッシュ,CaF2 ,Al(O
H)3 ,Mg(OH)2 ,Fe(OH)3 などの微細粒
子である汚泥スラリを含む低品位石膏を分離するには、
遠心分離機は高速回転のため遠心効果{Z=rω2 /
g、Z:遠心効果(−),r:回転半径(m),ω:角
速度(red/sec),g:重力の加速度(m/se
c2 )}が300〜800と大きい。これはケークに数
kg/cm2 〜十数kg/cm2 の圧力がかかることと
なり圧密される結果となる。そのためろ過特性を左右す
るろ過比抵抗(α)(m/kg)が大きくなってろ過速
度が低下する。従って同量のスラリを処理するためには
ろ過速度が遅くなった分、処理時間がかかり、遠心分離
機の基数を増やす必要がある。また回分式であるため、
その制御も複雑でメンテナンスも繁雑である。その点、
水平ベルト式真空脱水機は連続操作が可能で、また操作
圧力も300〜600mmHgの低圧力で操作するため
ケークの圧密も少なくろ過性もよい。The concentration of gypsum slurry by-produced in the wet lime-gypsum method flue gas desulfurization apparatus is about 20% by weight and the average particle size is as large as 30 to 50 μm. Is suitable for centrifugal separator, but the average particle size is 2 ~
Fly ash such as 10 μm, CaF 2 , Al (O
To separate low-grade gypsum containing sludge slurry which is fine particles such as H) 3 , Mg (OH) 2 , Fe (OH) 3 ,
The centrifugal separator rotates at high speed, so the centrifugal effect {Z = rω 2 /
g, Z: centrifugal effect (-), r: radius of gyration (m), ω: angular velocity (red / sec), g: acceleration of gravity (m / sec)
c 2 ) is as large as 300 to 800. This results to be consolidated will take the pressure of several kg / cm 2 ~ several tens of kg / cm 2 to cake. For this reason, the filtration specific resistance (α) (m / kg) which affects the filtration characteristics is increased, and the filtration speed is reduced. Therefore, in order to process the same amount of slurry, it takes time to process the reduced filtration speed, and it is necessary to increase the number of centrifuges. Also, because it is a batch type,
The control is complicated and the maintenance is complicated. That point,
The horizontal belt type vacuum dehydrator can be operated continuously, and the operation pressure is low, such as 300 to 600 mmHg.
【0008】また遠心分離機はろ過する際のオーバーチ
ャージ液中に数重量%の固形分を含むため、一度ろ液シ
ックナに送液し、固形分を沈降分離する必要があり、そ
のためろ液シックナ及び排水槽が必要であるが、水平ベ
ルト式真空脱水機の回収ろ液中の固形分が1000mg
/リットル程度であり、直接総合排水処理装置に返送す
ることが可能で設備費も低減でき経済的メリットが大き
い。Further, since the centrifugal separator contains several percent by weight of solids in the overcharged liquid at the time of filtration, it must be once sent to a filtrate thickener to separate the solids by sedimentation. And a drain tank is required, but the solid content in the recovered filtrate of the horizontal belt type vacuum dehydrator is 1000 mg.
Per liter, and can be returned directly to the integrated wastewater treatment equipment, reducing equipment costs and providing a great economic advantage.
【0009】水平ベルト式真空脱水機と言えども、2〜
10μmの微細粒子を含むスラリを処理する際には、長
時間使用するとろ布に目詰りを起こし、ろ過速度が低下
し効率が悪くなる。かかる欠点を解消するため、本発明
では先ず粒径の大きな石膏スラリでプレコート層を形成
させた後、粒径の小さな石膏スラリと汚泥スラリの混合
物を供給し、次いで洗浄及び脱水を行うようにした。こ
のように一定のプレコート層を形成することにより、粒
径の小さなスラリが供給されてもろ布に目詰りを起こす
ことなく、長時間安定したろ過速度が得られろ布の洗浄
工程をなくするか、あるいは洗浄間隔を長くすることが
でき非常に有効である。またろ過性がよいことからCl
- の洗浄も容易となる。[0009] Even though it is a horizontal belt type vacuum dehydrator,
When treating a slurry containing fine particles of 10 μm, if used for a long period of time, the filter cloth will be clogged, and the filtration speed will be reduced, resulting in poor efficiency. In order to solve such a drawback, in the present invention, after a pre-coat layer is first formed with a gypsum slurry having a large particle diameter, a mixture of a gypsum slurry and a sludge slurry having a small particle diameter is supplied, and then washing and dewatering are performed. . By forming a constant pre-coat layer in this way, a stable filtration rate can be obtained for a long time without causing clogging of the filter cloth even when a slurry having a small particle size is supplied. Alternatively, the cleaning interval can be lengthened, which is very effective. In addition, since the filterability is good, Cl
-Easy to clean.
【0010】[0010]
【実施例】図1により本発明の一実施態様を説明する。
湿式石灰石膏法排煙脱硫装置で副生する石膏スラリ1と
排水処理装置からの汚泥スラリ2が分離機供給槽3で混
合され、10〜15重量%のスラリとしてポンプ4で経
路5を経て水平ベルト式真空脱水機6に送液される。こ
の水平ベルト式真空脱水機6はドラム17,18を介し
て水平に設置された穴あきエンドレスベルト19でろ布
16を保持しており、スラリ供給室13にスラリを供給
した後、洗浄室14で上部から散布する洗浄水10でC
l- を洗浄した後、脱水室15で所定の含水率になるよ
う脱水され、ケークはろ布16から剥離され経路7から
ベルトコンベヤ8で所定の場所に移送され低品位石膏9
として回収される。FIG. 1 illustrates an embodiment of the present invention.
A gypsum slurry 1 produced as a by-product in a wet lime-gypsum flue gas desulfurization apparatus and a sludge slurry 2 from a wastewater treatment apparatus are mixed in a separator supply tank 3, and are mixed as a slurry of 10 to 15% by weight through a path 5 by a pump 4 via a path 5. The liquid is sent to the belt-type vacuum dehydrator 6. The horizontal belt type vacuum dehydrator 6 holds the filter cloth 16 by a perforated endless belt 19 installed horizontally via drums 17 and 18, supplies the slurry to a slurry supply chamber 13, and then supplies the slurry to a cleaning chamber 14. Cleaning water 10 sprayed from above with C
l - washed and dehydrated to a predetermined moisture content in the dehydration chamber 15, the cake is transferred to a predetermined location from the path 7 is peeled off from the filter cloth 16 by the belt conveyor 8 low-grade gypsum 9
Will be collected as
【0011】スラリ供給室13、洗浄室14、脱水室1
5は300〜600mmHgの真空が保たれる構造とな
っており、そこでろ過された液は経路11を介して、気
液分離器20に送液され、ろ液は経路25からろ液槽1
2に回収された後、ポンプ21で経路22を介して総合
排水処理装置へ返送される。一方、気液分離器20は経
路23を介してバキュームポンプ24で300〜600
mmHgの真空が保たれている。ろ布16はスラリをろ
過することにより目詰りを起すため、26からの洗浄水
または圧縮空気で逆洗し目詰りを防止している。排出さ
れた液は経路27でろ液槽12に戻される。本発明の如
く、遠心分離機のかわりに水平ベルト式真空脱水機を採
用することにより、連続操作が可能で、またケークも圧
密されることなく良好なろ過性をもつため、Cl- 洗浄
の効果も大きく、分離回収された低品位石膏中のCl-
濃度が100〜150mg/kg(ドライベース)、ま
た含水率20wt%以下の引取りメーカーの品質が満足
される。またろ液シックナなどの省略もでき設備費も低
減できる。Slurry supply chamber 13, washing chamber 14, dehydration chamber 1
5 has a structure in which a vacuum of 300 to 600 mmHg is maintained, and the filtered liquid is sent to a gas-liquid separator 20 via a path 11, and the filtrate is passed from a path 25 to a filtrate tank 1.
After being collected by the pump 2, it is returned to the integrated wastewater treatment device via the path 22 by the pump 21. On the other hand, the gas-liquid separator 20 is supplied to the vacuum pump 24 via
A vacuum of mmHg is maintained. Since the filter cloth 16 is clogged by filtering the slurry, the filter cloth 16 is backwashed with washing water or compressed air from 26 to prevent clogging. The discharged liquid is returned to the filtrate tank 12 via a path 27. As in the present invention, by employing the horizontal belt vacuum dehydrator instead of a centrifuge, it can be continuously operated, and because the cake also have good filterability without being compacted, Cl - cleaning effect is large, Cl low-grade gypsum is separated and recovered -
The quality of a pickup manufacturer with a concentration of 100 to 150 mg / kg (dry base) and a water content of 20 wt% or less is satisfied. In addition, it is possible to omit a filtrate thickener or the like, thereby reducing equipment costs.
【0012】低品位石膏の分離回収において、水平ベル
ト式脱水機を適用した際にろ布の目詰りを起こさず、長
期安定運転が可能な方法につき図2により説明する。こ
の方法は水平ベルト式脱水機の処理工程を改善すること
により、より効果の高い分離、回収方法を提供するもの
である。すなわち、水平ベルト式脱水機と言えども2〜
10μmの微粒子の汚泥スラリを含む低品位石膏の分離
に、繰り返しろ布を使用した場合にはろ布に目詰りが発
生し、ろ過速度が経時的に低下する。それを防止するた
めにろ布洗浄を実施しているが完全には除去することが
できず長時間使用するとろ過性が悪くなる。Referring to FIG. 2, a method for performing long-term stable operation without clogging of a filter cloth when a horizontal belt type dewatering machine is applied in the separation and recovery of low-grade gypsum will be described. This method provides a more effective separation and recovery method by improving the processing steps of the horizontal belt dehydrator. That is, even though it is a horizontal belt type dehydrator,
When a filter cloth is repeatedly used for separating low-grade gypsum containing sludge slurry of 10 μm fine particles, the filter cloth is clogged, and the filtration speed decreases with time. To prevent this, the filter cloth is washed, but it cannot be completely removed and the filterability deteriorates when used for a long time.
【0013】このような欠点を解消するため水平ベルト
式脱水機の処理工程を改善した。湿式石灰石膏法排煙脱
硫装置で副生する石膏スラリ1をバルブ30を通して経
路28から水平ベルト式脱水機6の石膏スラリ供給室3
4に供給し、5〜20mmの高品位の石膏によるプレコ
ート層を形成させる。なお高品位石膏はろ過性がよいた
め石膏スラリ供給室34の長さを大きくとる必要がなく
1〜2室で十分である。プレコート層が形成されれば、
次の工程のスラリ供給室13に移動する。一方、石膏ス
ラリ1と汚泥スラリ2をそれぞれバルブ32,33を介
して分離機供給槽3に供給混合し、ポンプ4によりバル
ブ35、経路5を介してスラリ供給室13に供給する。
石膏スラリ1でプレコート層が形成されているろ布16
上に汚泥スラリ2を含む低品位石膏スラリが供給される
ため、直接ろ布16の目詰りを起こすことがない。その
後、洗浄室14で上部から散布する洗浄水10でCl-
を洗浄し、脱水室15で所定の含水率になるよう脱水さ
れた後、低品位石膏9として分離回収される。その他の
操作は図1で説明したとおりである。従って、図1と同
一部位には同符号を付してあるので、その他の符号の説
明は省略する。In order to eliminate such a drawback, the processing steps of the horizontal belt type dehydrator have been improved. The gypsum slurry 1 by-produced in the wet lime-gypsum method flue gas desulfurization apparatus is passed through a valve 30 from a path 28 to a gypsum slurry supply chamber 3 of a horizontal belt dehydrator 6.
4 to form a pre-coated layer of high quality gypsum of 5 to 20 mm. In addition, since high-grade gypsum has good filterability, it is not necessary to increase the length of the gypsum slurry supply chamber 34, and one or two chambers are sufficient. Once the precoat layer is formed,
It moves to the slurry supply chamber 13 in the next step. On the other hand, the gypsum slurry 1 and the sludge slurry 2 are supplied and mixed to the separator supply tank 3 via the valves 32 and 33, respectively, and supplied to the slurry supply chamber 13 via the valve 35 and the path 5 by the pump 4.
Filter cloth 16 on which a precoat layer is formed with gypsum slurry 1
Since the low-grade gypsum slurry including the sludge slurry 2 is supplied thereon, the filter cloth 16 is not directly clogged. Thereafter, the cleaning water 10 sprayed from above in the cleaning chamber 14 is used to remove Cl −.
Is washed and dehydrated in the dehydration chamber 15 so as to have a predetermined water content, and then separated and collected as low-grade gypsum 9. Other operations are as described in FIG. Therefore, the same parts as those in FIG. 1 are denoted by the same reference numerals, and the description of the other reference numerals is omitted.
【0014】このように高品位石膏スラリでプレコート
層を形成さすことにより、ろ布16の目詰りが防止で
き、ろ布の逆洗を実施しなくてもよく、あるいは逆洗回
数を減じることができ、長時間安定したろ過速度が得ら
れ、ひいてはCl- 洗浄効果を高めることができた。な
お高品位石膏でプレコート層を形成しても、低品位石膏
に比べろ過速度が十数倍大きいため特に支障にはならな
い。By forming the precoat layer with the high-grade gypsum slurry in this manner, clogging of the filter cloth 16 can be prevented, and it is not necessary to perform backwashing of the filter cloth, or the number of times of backwashing can be reduced. As a result, a stable filtration rate was obtained for a long time, and the Cl - cleaning effect was able to be enhanced. In addition, even if the precoat layer is formed with high-grade gypsum, the filtration speed is ten and several times higher than that of low-grade gypsum, so that no problem is caused.
【0015】(実施例1)湿式石灰石膏法排煙脱硫装置
で副生する石膏純度98重量%の石膏スラリ(平均粒
径:32μm)と排水処理装置で発生する汚泥スラリを
混合し、石膏純度80重量%の低品位石膏を調製し加圧
式のリーフテスタでろ過圧力とろ過比抵抗の関係を測定
した。なお、上記汚泥スラリの性状は平均粒径:4.3
μm、その組成は重量%でCaSO4 ・2H2 O:1
4.6、CaCO3 :6.1、Al(OH)3 :28.
0、Fe(OH)3 :11.3、Mg(OH)2 :1.
4、CaF2 :3.8、SiO2 :31.6であった。
その結果を図3に示す。ここでろ過比抵抗は次の式で計
算した。 dV/dθ=gc ・ΔP・A/μ(Rc +Rm ) ・・・(1) Rc = α・W/A ・・・(2) V : ろ液体積 〔m3 〕 θ : ろ過時間 〔sec〕 A : ろ過面積 〔m2 〕 ΔP: ろ過圧力 〔kg/m2 〕 μ : ろ液粘度 〔kg/m・s〕 Rc : ケーキ抵抗係数 〔1/m〕 Rm : ろ機抵抗係数 〔1/m〕 gc : 重力換算係数 α : ろ過比抵抗 〔m/kg〕 W : ケーキ重量 〔dry−kg〕(Example 1) A gypsum slurry having a gypsum purity of 98% by weight (average particle diameter: 32 μm) produced as a by-product in a wet lime-gypsum method flue gas desulfurization apparatus and a sludge slurry generated in a wastewater treatment apparatus were mixed. 80% by weight of low-grade gypsum was prepared, and the relationship between filtration pressure and filtration specific resistance was measured with a pressurized leaf tester. The properties of the above sludge slurry were as follows: average particle size: 4.3
μm, the composition of which is expressed in weight% as CaSO 4 .2H 2 O: 1
4.6, CaCO 3 : 6.1, Al (OH) 3 : 28.
0, Fe (OH) 3 : 11.3, Mg (OH) 2 : 1.
4, CaF 2 : 3.8, SiO 2 : 31.6.
The result is shown in FIG. Here, the filtration specific resistance was calculated by the following equation. dV / dθ = g c · ΔP · A / μ (R c + R m) ··· (1) R c = α · W / A ··· (2) V: filtrate volume [m 3] theta: Filtration Time [sec] A: Filtration area [m 2 ] ΔP: Filtration pressure [kg / m 2 ] μ: Filtrate viscosity [kg / m · s] R c : Cake resistance coefficient [1 / m] R m : Filter Resistance coefficient [1 / m] g c : Gravity conversion coefficient α: Filtration specific resistance [m / kg] W: Cake weight [dry-kg]
【0016】図3からも明らかなように石膏純度98重
量%の高品位石膏に比べ、汚泥成分を混合し石膏純度8
0重量%に調製した低品位石膏のろ過比抵抗は50〜1
00倍大きくなる。このろ過比抵抗は(1)(2)式に
示すとおりろ過速度に反比例するものであり、ろ過比抵
抗が大きくなるほどろ過速度が遅くなる。また、石膏純
度の低い低品位石膏はろ過圧力(ΔP)が高くなるほど
ろ過比抵抗が大きくなり圧密される。従って低品位石膏
の分離に遠心分離機を採用すると前述したように遠心効
果が大きく、ケークに数kg/cm2 〜十数kg/cm
2 の圧力がかかることとなり、ろ過比抵抗が増しろ過し
にくくなる。そのため低品位石膏の分離・回収に長時間
を要することとなり、同量のスラリを処理するためには
遠心分離機の基数を増やす必要がある。一方、水平ベル
ト式真空脱水機は300〜600mmHgの低圧で操作
するため、圧密されることもなく、適当なケーク厚みを
選択することにより十分ろ過速度も確保できる。As is clear from FIG. 3, compared with high-grade gypsum having a gypsum purity of 98% by weight, the sludge component is mixed and the gypsum purity is 8%.
The filtration specific resistance of low-grade gypsum prepared to 0% by weight is 50 to 1
00 times larger. The filtration specific resistance is inversely proportional to the filtration speed as shown in the equations (1) and (2), and the filtration speed decreases as the filtration specific resistance increases. In addition, low-grade gypsum with low gypsum purity has higher filtration specific resistance and consolidation as the filtration pressure (ΔP) increases. Therefore, if a centrifugal separator is used for the separation of low-grade gypsum, the centrifugal effect is large as described above, and the cake is several kg / cm 2 to several tens of kg / cm.
The pressure of 2 is applied, which increases the filtration specific resistance and makes filtration difficult. Therefore, it takes a long time to separate and collect low-grade gypsum, and it is necessary to increase the number of centrifuges in order to treat the same amount of slurry. On the other hand, since the horizontal belt type vacuum dehydrator operates at a low pressure of 300 to 600 mmHg, a sufficient filtration speed can be secured by selecting an appropriate cake thickness without consolidation.
【0017】(実施例2)図1に示した本発明の方法及
び図5に示した従来方法を用いて分離機供給槽3で調製
した石膏純度90重量%の低品位石膏スラリを使用して
低品位石膏の分離回収及びCl- の洗浄試験を実施し
た。その結果を表1に示すが、本発明の水平ベルト式脱
水機を使用した場合には、Cl- 洗浄効果は95%以上
で低品位石膏中のCl- 濃度も100mg/kg(ドラ
イベース)以下及び含水率も15wt%と引取りメーカ
ーの品質を満足する結果を得た。比較例として実施した
遠心分離機はCl- 洗浄効果は95%以上で水平ベルト
式脱水機と同じであるが、洗浄水量比は1.7と多量の
水を要し、洗浄時間も長くかかった。但し、含水率は1
0wt%以下で脱水性は良好であり、水平ベルト式脱水
機は脱水性は若干劣っていた。従って低品位石膏の分離
回収において水平ベルト式脱水機を採用することによ
り、従来の遠心分離機に比べ性能的に劣るものではな
く、むしろ洗浄水量は少なくてすみ、また連続化が可能
で設備コスト的にも安くでき経済的メリットが大きい。(Example 2) Using a low-grade gypsum slurry having a gypsum purity of 90% by weight prepared in the separator supply tank 3 using the method of the present invention shown in FIG. 1 and the conventional method shown in FIG. separation and recovery and Cl low-grade gypsum - washing tests were carried out. The results are shown in Table 1. When the horizontal belt type dehydrator of the present invention was used, the Cl - cleaning effect was 95% or more and the Cl - concentration in low-grade gypsum was 100 mg / kg (dry base) or less. Also, the water content was 15 wt%, which was a result satisfying the quality of the collection manufacturer. The centrifugal separator used as a comparative example has a Cl - cleaning effect of 95% or more, which is the same as that of the horizontal belt dehydrator, but requires a large amount of water with a cleaning water ratio of 1.7 and requires a long cleaning time. . However, the water content is 1
At 0 wt% or less, the dewaterability was good, and the horizontal belt dehydrator was slightly inferior in dewaterability. Therefore, by adopting a horizontal belt type dewatering machine in the separation and recovery of low-grade gypsum, the performance is not inferior to that of a conventional centrifugal separator. It can be cheaper and has a great economic advantage.
【0018】[0018]
【表1】 Cl- 洗浄効率={1−(洗浄後のケーク中のCl- 濃
度/洗浄なしのケーク中のCl- 濃度)}×100
(%) 洗浄水量比=洗浄水量(kg/h)/低品位石膏ケーク
量(kg/h)[Table 1] Cl - cleaning efficiency = {1- (Cl in cake after washing - Cl in cake without concentration / washing - concentration)} × 100
(%) Wash water amount ratio = Wash water amount (kg / h) / Low-grade gypsum cake amount (kg / h)
【0019】こゝで使用した脱水機の仕様及び運転条件
は次のとおりである。 (1)水平ベルト式脱水機 (a)ろ過面積 : 0.3m2 (b)真空圧力 : −500mmHg (c)脱水時間 : 120sec (d)使用ろ布 : N−0091(大機ゴム工業社
製:商品名) (e)ケーク厚み: 20mm (2)遠心分離機 (a)バスケット仕様 : φ485×200H×φ3
85mm (b)バスケット容量 : MAX 13.7リットル (c)回転数 : 1415rpm (d)遠心効果 : 544G (e)ケーク厚さ : 50mm (f)平均ろ過面積 : 0.273m2 (g)脱水時間 : 120secThe specifications and operating conditions of the dehydrator used here are as follows. (1) Horizontal belt type dehydrator (a) Filtration area: 0.3 m 2 (b) Vacuum pressure: -500 mmHg (c) Dehydration time: 120 sec (d) Filter cloth used: N-0091 (manufactured by Daiki Rubber Industry Co., Ltd.) : Product name) (e) Cake thickness: 20mm (2) Centrifuge (a) Basket specification: φ485 × 200H × φ3
85 mm (b) Basket capacity: MAX 13.7 liters (c) Rotational speed: 1415 rpm (d) Centrifugal effect: 544 G (e) Cake thickness: 50 mm (f) Average filtration area: 0.273 m 2 (g) Dewatering time : 120 sec
【0020】(実施例3)図1に示す本発明の方法を用
い、分離機供給槽からの低品位石膏スラリ(石膏純度8
5重量%)を20mm厚さのケーク層になるように供給
し、洗浄、脱水、ケークの分離を順次行うと共にろ布洗
浄を実施しながら長時間運転し、ろ過速度の低下割合を
調べた。一方、図2に示す本発明の方法を用い高品位石
膏スラリ(石膏純度98重量%)で先ずプレコート層を
5mmの厚さで形成させた後、分離機供給槽からの低品
位石膏スラリ(石膏純度85重量%)を供給し、合計ケ
ーク厚さを25mmとした後、洗浄、脱水、ケークの分
離を順次行いろ過速度の低下割合を比較検討した。Example 3 Using the method of the present invention shown in FIG. 1, a low-grade gypsum slurry (gypsum purity 8
(5% by weight) was supplied so as to form a cake layer having a thickness of 20 mm, and washing, dehydration, and separation of the cake were successively performed, and the filter cloth was washed for a long time, and the rate of decrease in filtration speed was examined. On the other hand, a high-grade gypsum slurry (gypsum purity: 98% by weight) is used to first form a precoat layer with a thickness of 5 mm using the method of the present invention shown in FIG. 2, and then a low-grade gypsum slurry (gypsum) from a separator supply tank is formed. (Purity: 85% by weight), and the total cake thickness was adjusted to 25 mm. After that, washing, dehydration, and separation of the cake were sequentially performed, and the reduction rate of the filtration rate was compared and examined.
【0021】その結果を図4に示す。また水平ベルト式
脱水機の仕様及び運転条件を表2に示す。図4からも明
らかなように高品位石膏でプレコート層を形成する方式
においては、長時間使用してもろ過速度の低下はほとん
どなく、ろ布の目詰りが発生しにくいため長期間の安定
運転が可能となった。FIG. 4 shows the result. Table 2 shows the specifications and operating conditions of the horizontal belt dehydrator. As is clear from FIG. 4, in the method of forming the precoat layer with high-grade gypsum, the filtration speed hardly decreases even when used for a long time, and clogging of the filter cloth hardly occurs. Became possible.
【0022】[0022]
【表2】 [Table 2]
【0023】[0023]
【発明の効果】以上のように本発明は従来方法に比べ、
ケーク層が圧密されないため十分なろ過速度が確保でき
ると共に、連続操作が可能で設備がシンプルで安価とな
る。また、Cl- 洗浄効果は従来方法に比べ少ない洗浄
水量で従来装置と同等の性能が得られる。また、長時間
の使用においても、水平ベルト式脱水機のろ布の目詰り
が少なく安定運転が可能となる。従って本発明は湿式石
灰石膏法排煙脱硫装置で副生する石膏スラリの一部と同
装置に付属する排水処理装置から発生する汚泥スラリを
混合し、低品位石膏を分離回収する方法として設備的に
安価で高性能な分離回収を可能とする。As described above, the present invention is more effective than the conventional method.
Since the cake layer is not compacted, a sufficient filtration rate can be ensured, and continuous operation is possible, and the equipment is simple and inexpensive. Furthermore, Cl - cleaning effect conventional apparatus equivalent performance is obtained with a small amount of wash water as compared with the conventional method. In addition, even when used for a long time, the filter cloth of the horizontal belt type dehydrator can be stably operated with less clogging. Accordingly, the present invention provides a method for separating and recovering low-grade gypsum by mixing a part of gypsum slurry produced as a by-product in a wet lime gypsum method flue gas desulfurization apparatus and sludge slurry generated from a wastewater treatment apparatus attached to the apparatus. Inexpensive and high-performance separation and recovery are possible.
【図1】本発明の第1実施例に係るシステムフローの説
明図。FIG. 1 is an explanatory diagram of a system flow according to a first embodiment of the present invention.
【図2】本発明の第2実施例に係るシステムフローの説
明図。FIG. 2 is an explanatory diagram of a system flow according to a second embodiment of the present invention.
【図3】石膏純度によるろ過圧力とろ過比抵抗の関係を
示す図表。FIG. 3 is a chart showing the relationship between filtration pressure and filtration specific resistance depending on gypsum purity.
【図4】第1実施例と第2実施例の運転時間とろ過速度
の低下割合を示す図表。FIG. 4 is a table showing the operation time and the reduction rate of the filtration speed in the first embodiment and the second embodiment.
【図5】従来の低品位石膏分離回収法のシステムフロー
の説明図。FIG. 5 is an explanatory diagram of a system flow of a conventional low-grade gypsum separation and recovery method.
───────────────────────────────────────────────────── フロントページの続き (58)調査した分野(Int.Cl.7,DB名) C04B 11/26 B01D 53/50 B01D 53/77 ──────────────────────────────────────────────────続 き Continued on the front page (58) Field surveyed (Int.Cl. 7 , DB name) C04B 11/26 B01D 53/50 B01D 53/77
Claims (2)
石膏スラリの一部と同装置に付属する排水処理装置から
発生する汚泥スラリとを混合して低品位石膏を分離回収
する方法において、該混合スラリを水平ベルト式真空脱
水機で処理することを特徴とする低品位石膏分離回収方
法。1. A method for separating and recovering low-grade gypsum by mixing a part of gypsum slurry by-produced in a wet lime-gypsum method flue gas desulfurization apparatus and a sludge slurry generated from a wastewater treatment apparatus attached to the apparatus. And treating the mixed slurry with a horizontal belt vacuum dehydrator.
石膏スラリでプレコート層を形成することを特徴とする
請求項1記載の低品位石膏分離回収方法。2. The method for separating and recovering low-grade gypsum according to claim 1, wherein a precoat layer is previously formed on the belt of the horizontal belt type vacuum dehydrator with gypsum slurry.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP06146141A JP3110251B2 (en) | 1994-06-28 | 1994-06-28 | Low-grade gypsum separation and recovery method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP06146141A JP3110251B2 (en) | 1994-06-28 | 1994-06-28 | Low-grade gypsum separation and recovery method |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH0812389A JPH0812389A (en) | 1996-01-16 |
| JP3110251B2 true JP3110251B2 (en) | 2000-11-20 |
Family
ID=15401076
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| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP06146141A Expired - Fee Related JP3110251B2 (en) | 1994-06-28 | 1994-06-28 | Low-grade gypsum separation and recovery method |
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| Country | Link |
|---|---|
| JP (1) | JP3110251B2 (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH0545312U (en) * | 1991-11-20 | 1993-06-18 | 三菱自動車工業株式会社 | Damping gear |
Families Citing this family (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP4672154B2 (en) * | 2001-02-06 | 2011-04-20 | 三菱重工業株式会社 | Waste water treatment method and waste water treatment equipment |
| FI121312B (en) | 2005-10-18 | 2010-09-30 | Metso Power Oy | A method for treating flue gases |
| JP5502920B2 (en) * | 2012-03-14 | 2014-05-28 | 株式会社東芝 | Fluorine recovery device and fluorine recovery method |
| JP5502924B2 (en) * | 2012-03-30 | 2014-05-28 | 株式会社東芝 | Water treatment method |
| JP5649749B2 (en) * | 2014-01-31 | 2015-01-07 | 株式会社東芝 | Water treatment method |
| CN113171675B (en) * | 2020-03-06 | 2025-06-10 | 大唐环境产业集团股份有限公司 | Desulfurization gypsum grading cleaning device and cleaning method |
| CN115990400A (en) * | 2021-10-18 | 2023-04-21 | 中国石油化工股份有限公司 | A method for reducing the moisture content of flue gas desulfurization gypsum products |
| CN115557719B (en) * | 2022-08-16 | 2023-08-15 | 湖北祥云(集团)化工股份有限公司 | Comprehensive treatment method of phosphogypsum |
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1994
- 1994-06-28 JP JP06146141A patent/JP3110251B2/en not_active Expired - Fee Related
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH0545312U (en) * | 1991-11-20 | 1993-06-18 | 三菱自動車工業株式会社 | Damping gear |
Also Published As
| Publication number | Publication date |
|---|---|
| JPH0812389A (en) | 1996-01-16 |
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