JP3133272B2 - Method for estimating suspended solids concentration and evaporating and concentrating desulfurization wastewater - Google Patents
Method for estimating suspended solids concentration and evaporating and concentrating desulfurization wastewaterInfo
- Publication number
- JP3133272B2 JP3133272B2 JP09075131A JP7513197A JP3133272B2 JP 3133272 B2 JP3133272 B2 JP 3133272B2 JP 09075131 A JP09075131 A JP 09075131A JP 7513197 A JP7513197 A JP 7513197A JP 3133272 B2 JP3133272 B2 JP 3133272B2
- Authority
- JP
- Japan
- Prior art keywords
- concentration
- evaporation residue
- temperature
- boiling point
- suspended substance
- 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
- 238000001704 evaporation Methods 0.000 title claims description 65
- 238000000034 method Methods 0.000 title claims description 49
- 239000007787 solid Substances 0.000 title claims description 28
- 238000006477 desulfuration reaction Methods 0.000 title claims description 22
- 230000023556 desulfurization Effects 0.000 title claims description 22
- 239000002351 wastewater Substances 0.000 title claims description 21
- 239000000126 substance Substances 0.000 claims description 53
- 230000008020 evaporation Effects 0.000 claims description 50
- 238000009835 boiling Methods 0.000 claims description 35
- 230000005484 gravity Effects 0.000 claims description 27
- 239000007788 liquid Substances 0.000 claims description 23
- 239000000725 suspension Substances 0.000 claims description 5
- 239000000243 solution Substances 0.000 description 35
- 239000013078 crystal Substances 0.000 description 11
- 239000012141 concentrate Substances 0.000 description 9
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 5
- 239000003546 flue gas Substances 0.000 description 5
- 238000010438 heat treatment Methods 0.000 description 4
- 230000000630 rising effect Effects 0.000 description 4
- 150000003839 salts Chemical class 0.000 description 4
- 239000000498 cooling water Substances 0.000 description 3
- 238000001914 filtration Methods 0.000 description 3
- 238000004062 sedimentation Methods 0.000 description 3
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 3
- OSGAYBCDTDRGGQ-UHFFFAOYSA-L calcium sulfate Chemical compound [Ca+2].[O-]S([O-])(=O)=O OSGAYBCDTDRGGQ-UHFFFAOYSA-L 0.000 description 2
- 238000005345 coagulation Methods 0.000 description 2
- 230000015271 coagulation Effects 0.000 description 2
- 229910052602 gypsum Inorganic materials 0.000 description 2
- 239000010440 gypsum Substances 0.000 description 2
- 238000002347 injection Methods 0.000 description 2
- 239000007924 injection Substances 0.000 description 2
- 238000005259 measurement Methods 0.000 description 2
- 125000000962 organic group Chemical group 0.000 description 2
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 description 1
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 description 1
- FYYHWMGAXLPEAU-UHFFFAOYSA-N Magnesium Chemical compound [Mg] FYYHWMGAXLPEAU-UHFFFAOYSA-N 0.000 description 1
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 230000002378 acidificating effect Effects 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- 229910052791 calcium Inorganic materials 0.000 description 1
- 239000011575 calcium Substances 0.000 description 1
- 239000000701 coagulant Substances 0.000 description 1
- 230000006835 compression Effects 0.000 description 1
- 238000007906 compression Methods 0.000 description 1
- 230000002596 correlated effect Effects 0.000 description 1
- 230000003009 desulfurizing effect Effects 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 230000008030 elimination Effects 0.000 description 1
- 238000003379 elimination reaction Methods 0.000 description 1
- 239000012530 fluid Substances 0.000 description 1
- 229910017053 inorganic salt Inorganic materials 0.000 description 1
- 238000009434 installation Methods 0.000 description 1
- 229910052749 magnesium Inorganic materials 0.000 description 1
- 239000011777 magnesium Substances 0.000 description 1
- 230000007935 neutral effect Effects 0.000 description 1
- 238000010979 pH adjustment Methods 0.000 description 1
- 230000002265 prevention Effects 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
- 239000010802 sludge Substances 0.000 description 1
- 239000000779 smoke Substances 0.000 description 1
- 238000010998 test method Methods 0.000 description 1
- 238000012360 testing method Methods 0.000 description 1
- 239000010409 thin film Substances 0.000 description 1
Landscapes
- Investigating Or Analyzing Materials Using Thermal Means (AREA)
- Treating Waste Gases (AREA)
- Heat Treatment Of Water, Waste Water Or Sewage (AREA)
- Vaporization, Distillation, Condensation, Sublimation, And Cold Traps (AREA)
Description
【0001】[0001]
【発明の属する技術分野】本発明は、塩類が溶解してい
る溶液中の懸濁物質の濃度をリアルタイムに推定する方
法に関するものである。The present invention relates to a method for estimating the concentration of a suspended substance in a solution in which salts are dissolved in real time.
【0002】[0002]
【従来の技術】排煙脱硫排水は、硫酸カルシウム等の無
機塩が溶解しており、排煙脱硫排水を処理する方法とし
て、2段凝集沈殿濾過法等の凝集剤を添加して沈殿濾過
する方法と、蒸発濃縮により水分を蒸発させる方法があ
る。蒸発濃縮法は、2段凝集沈殿濾過法と比べて、処理
効率が高く、薬品使用量が少ないことに起因して汚泥の
発生量が少なく、さらに装置の設置面積を低減できる等
の利点があり、近年において排煙脱硫排水の処理方法と
して注目されるようになっている。BACKGROUND OF THE INVENTION Flue gas desulfurization effluent contains an inorganic salt such as calcium sulfate dissolved therein. As a method of treating the flue gas desulfurization effluent, a coagulant such as a two-stage coagulation sedimentation filtration method is added to carry out sedimentation filtration. There are a method and a method of evaporating water by evaporative concentration. The evaporative concentration method has advantages over the two-stage coagulation sedimentation filtration method in that the treatment efficiency is high, the amount of sludge generated is small due to the small amount of chemical used, and the installation area of the apparatus can be reduced. In recent years, it has attracted attention as a method for treating flue gas desulfurization wastewater.
【0003】しかしながら蒸発濃縮法は、蒸発濃縮装置
で排煙脱硫排水の水分を蒸発させて濃縮するため、濃縮
工程において排煙脱硫排水中に含まれるスケール成分が
蒸発濃縮装置内の伝熱管等に付着しやすいという欠点が
ある。スケール付着を防止する方法として様々な技術が
提案されているが、その中に種晶を添加して蒸発濃縮を
行い、スケール成分を種晶に付着させたり、濃縮液中に
析出させて伝熱管等の表面へのスケール付着を防止する
方法がある。However, in the evaporative concentration method, since the moisture in the flue gas desulfurization wastewater is evaporated and concentrated by the evaporative concentration device, the scale component contained in the flue gas desulfurization wastewater in the concentration step is transferred to a heat transfer tube or the like in the evaporative concentration device. There is a disadvantage that it is easily attached. Various techniques have been proposed as a method for preventing scale adhesion.However, a seed crystal is added to the solution to perform evaporation and concentration, and the scale component is attached to the seed crystal or precipitated in a concentrated solution to form a heat transfer tube. There is a method of preventing the scale from adhering to the surface.
【0004】種晶を添加する方法は、蒸発濃縮装置内で
循環する濃縮液中の種晶の濃度を5〜25wt%程度に
維持する必要がある。濃縮液中の種晶の濃度が上記範囲
を外れると、スケール防止効果が低下するので、濃縮液
中の種晶の濃度、すなわち濃縮液中の懸濁物質の濃度を
正確に測定し、懸濁物質の濃度を管理する必要がある。[0004] In the method of adding seed crystals, it is necessary to maintain the concentration of the seed crystals in the concentrated liquid circulating in the evaporative concentration apparatus at about 5 to 25 wt%. If the concentration of the seed crystal in the concentrate is out of the above range, the scale prevention effect is reduced, so that the concentration of the seed crystal in the concentrate, that is, the concentration of the suspended substance in the concentrate is accurately measured, and the suspension is measured. It is necessary to control the concentration of the substance.
【0005】蒸発濃縮装置内で循環される濃縮液の濃度
管理は、一般にJISK0102(「工場排水試験方
法」)の懸濁物質及び蒸発残留物の測定法に準じて行わ
れる。濃縮液の濃度を測定するには、あらかじめ比重計
指示値と懸濁物質および蒸発残留物の相関関係を求めて
おき、濃縮液の比重から濃縮液の濃度を算出するもので
ある。[0005] The concentration of the concentrated liquid circulated in the evaporative concentration apparatus is generally controlled in accordance with the method for measuring suspended solids and evaporation residues according to JIS K0102 ("Method of testing wastewater from factories"). In order to measure the concentration of the concentrated liquid, the correlation between the indicated value of the hydrometer and the suspended substance and the evaporation residue is determined in advance, and the concentration of the concentrated liquid is calculated from the specific gravity of the concentrated liquid.
【0006】しかしながら、比重計では懸濁物質と溶解
性蒸発残留物を合わせた濃度を測定しており、懸濁物質
濃度を単独で測定することができない。[0006] However, the hydrometer does not allow the suspended substance to dissolve.
The combined concentration of the volatile residues is measured and the suspended solids concentration cannot be measured alone.
【0007】濃縮液中の懸濁物質の濃度を測定する方法
として濁度計を用いる方法もあるが、濁度計を用いる場
合は、通常5wt%程度の濃度を測定するのが上限であ
り、5wt%を越える濃度の濃縮液を測定するには、濃
縮液を希釈する必要がある。従って、リアルタイムに濃
縮液中の懸濁物質濃度を測定することは困難であった。As a method for measuring the concentration of the suspended substance in the concentrated liquid, there is a method using a turbidity meter. In the case of using a turbidity meter, the upper limit is usually to measure a concentration of about 5 wt%. In order to measure a concentrated solution having a concentration exceeding 5 wt%, it is necessary to dilute the concentrated solution. Therefore, it was difficult to measure the concentration of the suspended substance in the concentrate in real time.
【0008】[0008]
【発明が解決しようとする課題】本発明が解決しようと
する課題は、溶解性蒸発残留物および懸濁物質を含む溶
液中の懸濁物質濃度、特にスケーリング防止のために種
晶を添加する排煙脱硫排水の蒸発濃縮法において重要な
種晶(懸濁物質)濃度を、リアルタイムに自動的に広範
囲にかつ精度よく推定できる方法および脱硫排水をスケ
ールを付着させずに蒸発濃縮する方法を提供することで
ある。The problem to be solved by the present invention is that the concentration of suspended solids in a solution containing soluble evaporation residues and suspended solids, in particular, the elimination of seeds to prevent scaling. Provided are a method for automatically and in real time estimating the concentration of seed crystals (suspended substances), which is important in the evaporative concentration method of smoke desulfurization wastewater, in real time, and a method for evaporating and desulfurizing wastewater without attaching scale. That is.
【0009】[0009]
【課題を解決するための手段】本発明者らは、塩類が溶
解した溶液の沸点は塩類の存在により上昇することに着
目し、本発明を完成するに至った。Means for Solving the Problems The present inventors have noticed that the boiling point of a solution in which salts are dissolved rises due to the presence of salts, and have completed the present invention.
【0010】すなわち、本発明は、 (1) 溶解性蒸発残留物および懸濁物質を含む溶液の
懸濁物質濃度を推定する方法において、予め全蒸発残留
物と溶液の比重との相関式(1) 全蒸発残留物(wt%)=f(比重) …… (1) を求め、さらに溶解性蒸発残留物と沸点上昇温度との相
関式(2) 溶解性蒸発残留物(wt%)=f(沸点上昇温度) …… (2) を求め、溶解性蒸発残留物および懸濁物質を含む溶液の
比重と沸点上昇温度を測定し、測定した比重と沸点上昇
温度を式(3) 懸濁物質(wt%)=f(比重)−f(沸点上昇温度) …… (3) に代入して演算することを特徴とする溶解性蒸発残留物
および懸濁物質を含む溶液の懸濁物質濃度の推定方法、 (2) 沸点上昇温度を、溶液温度および発生蒸気温度
を測定して、式(4) 沸点上昇温度(℃)=溶液温度(℃)−発生蒸気温度(℃) …… (4) により求めることを特徴とする前記(1)項に記載の懸
濁物質濃度の推定方法、 (3) 溶解性蒸発残留物および懸濁物質を含む溶液
が、溶解性蒸発残留物および懸濁物質を含む脱硫排水で
ある前記(1)項または(2)項に記載の懸濁物質濃度
の推定方法、 (4) 溶解性蒸発残留物および懸濁物質を含む脱硫排
水を循環して蒸発濃縮する方法において、前記(1)記
載の方法により蒸発濃縮液中の懸濁物質濃度を推定し、
懸濁物質濃度を5wt%〜25wt%に維持することを
特徴とする脱硫排水の蒸発濃縮方法、に関するものであ
る。That is, the present invention provides: (1) A method for estimating the concentration of suspended solids in a solution containing soluble evaporated residues and suspended substances, the method comprising: ) Total evaporation residue (wt%) = f (specific gravity) (1) is obtained, and the correlation equation between the soluble evaporation residue and the boiling point rise temperature (2) Soluble evaporation residue (wt%) = f (Boiling point rise temperature) …… (2) is determined, the specific gravity and the boiling point rise temperature of the solution containing the soluble evaporation residue and the suspended substance are measured, and the measured specific gravity and the boiling point rise temperature are expressed by the formula (3) (wt%) = f (specific gravity) -f (boiling temperature increase) .... of the solution containing the soluble evaporation residue <br/> and suspended matter, characterized in that assignment to calculating the (3) suspension Estimation method of suspended matter concentration, (2) Measure boiling point temperature, solution temperature and generated steam temperature (4) The method for estimating the concentration of suspended solids according to the above item (1), wherein the temperature is determined by the following equation: , (3) a solution containing a soluble evaporation residue and suspended solids, suspended solids concentration as described in (1) or (2) of a desulfurization waste water containing soluble evaporation residue and suspended solids (4) a method of evaporating and concentrating by circulating desulfurization wastewater containing a soluble evaporation residue and a suspended substance, wherein the concentration of the suspended substance in the evaporative concentrate is estimated by the method described in (1) above. ,
The present invention relates to a method for evaporating and condensing desulfurized wastewater, wherein the concentration of suspended solids is maintained at 5 wt% to 25 wt%.
【0011】[0011]
【発明の実施の形態】本発明方法は、塩類を溶解した溶
液の沸点が上昇することに着目してなされたものであ
る。まず、予め測定しようとする溶解性蒸発残留物およ
び懸濁物質を含む溶液の溶解性蒸発残留物と懸濁物質の
合計量すなわち全蒸発残留物と溶液の比重との相関関係
を求め、比重を独立変数とする相関式(1) 全蒸発残留物(wt%)=f(比重) …… (1) を求めておく。BEST MODE FOR CARRYING OUT THE INVENTION The method of the present invention has been made focusing on the fact that the boiling point of a solution in which salts are dissolved increases. First, the total amount of the soluble evaporation residue and the suspended substance in the solution containing the suspended evaporation residue and the suspended substance to be measured in advance, that is, the correlation between the total evaporation residue and the specific gravity of the solution The relationship is determined, and the correlation equation (1) using specific gravity as an independent variable, total evaporation residue (wt%) = f (specific gravity) (1) is determined in advance.
【0012】一方、溶解性蒸発残留物の存在により、溶
液の沸点が上昇するので、予め測定しようとする溶解性
蒸発残留物および懸濁物質を含む溶液の沸点上昇温度と
溶解性蒸発残留物濃度との相関関係を求め、沸点上昇温
度を独立変数とする相関式(2) 溶解性蒸発残留物(wt%)=f(沸点上昇温度) …… (2) を求めておく。On the other hand, the boiling point of the solution rises due to the presence of the soluble evaporation residue .
The boiling point of the solution containing evaporation residues and suspended solids
The correlation with the concentration of the soluble evaporation residue is determined, and the correlation equation (2) using the boiling point rising temperature as an independent variable is determined. Soluble evaporation residue (wt%) = f (boiling point rising temperature) (2) deep.
【0013】次いで、実際に懸濁物質濃度を推定しよう
とする溶液の比重と、沸点上昇温度を測定し、上記相関
式に代入し、全蒸発残留物と溶解性蒸発残留物の濃度を
求める。全蒸発残留物から溶解性蒸発残留物の濃度を引
いた値が懸濁物質の濃度であるので、下記式(3)によ
り懸濁物質濃度を算出することができる。Next, the specific gravity of the solution whose boiling point concentration is to be actually estimated and the boiling point rise temperature are measured and substituted into the above-mentioned correlation equation to determine the concentrations of the total evaporation residue and the soluble evaporation residue. Since the value obtained by subtracting the concentration of the soluble evaporation residue from the total evaporation residue is the concentration of the suspended substance, the concentration of the suspended substance can be calculated by the following equation (3).
【0014】 懸濁物質(wt%)=f(比重)−f(沸点上昇温度) …… (3) このようにして、溶解性蒸発残留物と懸濁物質を含む溶
液の比重と沸点上昇温度を測定することにより、リアル
タイムに溶液中の懸濁物質濃度を推定することができ
る。Suspended substance (wt%) = f (specific gravity) −f (boiling point rising temperature) (3) In this way, specific gravity and boiling point rising temperature of a solution containing a soluble evaporation residue and a suspended substance Is measured, the concentration of the suspended substance in the solution can be estimated in real time.
【0015】本発明方法において、沸点上昇温度を測定
するには、溶解性蒸発残留物および懸濁物質を含む溶液
の沸点を測定し、溶解性蒸発残留物および懸濁物質を含
まない溶液の沸点との差を求めてもよいが、溶解性蒸発
残留物および懸濁物質を含む溶液の温度と溶液の発生蒸
気温度を測定して、式(4) 沸点上昇温度(℃)=溶液温度(℃)−発生蒸気温度(℃) …… (4) により求める方が、沸点上昇温度をリアルタイムに計測
できる点で好ましい。[0015] In the method of the present invention, to measure the boiling temperature increase the solubility evaporation residue and measuring the boiling point of the solution containing the suspended matter, the boiling point of the solution containing no soluble evaporation residue and suspended solids May be determined, but the solubility evaporation
The temperature of the solution containing the residue and the suspended substance and the generated steam temperature of the solution are measured, and the equation (4): Boiling point rise temperature (° C.) = Solution temperature (° C.) − Generated steam temperature (° C.) (4) Is more preferable in that the boiling temperature can be measured in real time.
【0016】本発明方法において、比重を測定する方法
は、特に限定されないが、コリオリ式や差圧式の比重計
が電気信号による計測処理ができる点で好ましい。In the method of the present invention, the method for measuring the specific gravity is not particularly limited, but a Coriolis type or differential pressure type specific gravity meter is preferable because it can perform a measurement process using an electric signal.
【0017】請求項1に記載の方法は、溶解性蒸発残留
物および懸濁物質を含む溶液であれば、溶解性蒸発残留
物、懸濁物質および溶液の種類を問わず懸濁物質の濃度
を推定できる方法であるが、特に、脱硫排水を蒸発濃縮
する場合において、マグネシウム、カルシウム、塩化物
イオン、硫酸イオン等の溶解性蒸発残留物と石膏(セッ
コウ)等の懸濁物質(種晶)を含む濃縮液中の懸濁物質
(種晶)の濃度をリアルタイムに管理できるので特に有
効である。[0017] The method of claim 1, soluble evaporation residue
If a solution containing mono- and suspended matter, soluble evaporation residue
This method is capable of estimating the concentration of suspended solids regardless of the type of solids , suspended solids, and solutions. Particularly, when desulfurization wastewater is evaporated and concentrated, the solubility of magnesium, calcium, chloride ions, sulfate ions, etc. This is particularly effective because the concentration of the suspended substance (seed crystal) in the concentrated liquid containing the evaporation residue and the suspended substance (seed crystal) such as gypsum (gypsum) can be controlled in real time.
【0018】本発明の懸濁物質濃度を推定する方法は、
計測、演算を手動で行ってもよいが、予め求めた相関式
の式(1)、式(2)、式(3)と溶液温度と発生蒸気
温度から沸点上昇温度を求める式(4)を格納する記憶
部と、測定した比重、溶液温度、発生蒸気温度から式
(3)および式(4)により懸濁物質濃度を推定する演
算部を有する懸濁物質濃度推定装置により、自動的に推
定してもよい。The method for estimating the concentration of suspended solids according to the present invention comprises:
The measurement and the calculation may be performed manually, but the equations (1), (2), and (3) of the correlation equation obtained in advance and the equation (4) for obtaining the boiling point rise temperature from the solution temperature and the generated steam temperature are used. Automatically estimated by a storage substance concentration estimating device having a storage section for storing and a calculation section for estimating the concentration of the suspended substance from the measured specific gravity, solution temperature, and generated steam temperature by the equations (3) and (4). May be.
【0019】以下、図1のフロー図にそって、脱硫排水
を蒸発濃縮する方法について説明する。請求項4に記載
の発明は、脱硫排水を蒸発濃縮する方法であるが、蒸発
濃縮する手段は特に限定されるものではなく、例えば蒸
発濃縮器は、水平伝熱管方式でも、竪型の薄膜方式でも
よい。また、加熱も、外部加熱方式でも、自己蒸気圧縮
型でもよい。Hereinafter, a method for evaporating and condensing desulfurization wastewater will be described with reference to the flowchart of FIG. The invention according to claim 4 is a method for evaporating and condensing desulfurization wastewater, but the means for evaporating and condensing is not particularly limited. For example, the evaporating concentrator may be a horizontal heat transfer tube system or a vertical thin film system. May be. The heating may be of an external heating type or a self-vapor compression type.
【0020】脱硫排水は、排水供給ラインaaよりpH
調整槽1にため、酸あるいはアルカリを貯蔵しているp
H調整薬品槽5から注入ポンプ8を介してpH調整薬品
を注入し、脱硫排水のpHを弱酸性から中性になるよう
に調整する。The desulfurization effluent is supplied from the effluent supply line aa
P which stores acid or alkali for adjustment tank 1
A pH-adjusting chemical is injected from the H-adjusting chemical tank 5 via an injection pump 8 to adjust the pH of the desulfurization effluent from weakly acidic to neutral.
【0021】pH調整した脱硫排水を供給ポンプ9を介
して蒸発濃縮器2に供給する。蒸発濃縮器2はコンデン
サ3を介して真空ポンプ11により約−500mmHg
の減圧状態とし、加熱蒸気ラインbbより供給される蒸
気を伝熱管(図示せず)に供給して熱源とし、運転温度
は約70℃とする。The desulfurized wastewater whose pH has been adjusted is supplied to the evaporative concentrator 2 via a supply pump 9. The evaporating concentrator 2 is supplied with a vacuum pump 11 through the condenser 3 to about -500 mmHg.
, And the steam supplied from the heating steam line bb is supplied to a heat transfer tube (not shown) to serve as a heat source, and the operating temperature is set to about 70 ° C.
【0022】蒸発濃縮器2で蒸発した蒸気は、温度計7
で発生蒸気温度を測定し、コンデンサ3で凝縮し、凝縮
水ポンプ12により系外に排出する。ラインcc、dd
はコンデンサ3に出入りする冷却水のラインである。The vapor evaporated by the evaporator 2 is sent to a thermometer 7
The condensed water pump 12 discharges the generated steam to the outside of the system. Line cc, dd
Is a line for cooling water flowing into and out of the condenser 3.
【0023】一方、蒸発濃縮器2で濃縮された濃縮液
は、濃縮液循環ポンプ10および切り替え弁15により
蒸発濃縮器2へ循環されるが、循環する途中で比重計1
4および温度計6により、濃縮液の比重および温度を測
定する。循環しながら濃縮された濃縮液が一定の濃度に
達したら、切り替え弁15により流路を切り替え、濃縮
液タンク4に排出する。また、加熱蒸気のドレンは蒸気
ドレンポンプ13により排出される。On the other hand, the concentrated liquid concentrated in the evaporative concentrator 2 is circulated to the evaporative concentrator 2 by the concentrated liquid circulating pump 10 and the switching valve 15.
The specific gravity and the temperature of the concentrate are measured by 4 and a thermometer 6. When the concentrated liquid concentrated while circulating reaches a certain concentration, the flow path is switched by the switching valve 15 and discharged to the concentrated liquid tank 4. The drain of the heated steam is discharged by the steam drain pump 13.
【0024】脱硫排水については、予め全蒸発残留物と
比重との相関式および溶解性蒸発残留物と沸点上昇温度
との相関関係を求めておく。For the desulfurization wastewater, the correlation between the total evaporation residue and the specific gravity and the correlation between the soluble evaporation residue and the boiling point rise temperature are determined in advance.
【0025】濃縮循環中の濃縮液温度と発生蒸気温度か
ら前記式(4)により沸点上昇温度を求め、さらに測定
した濃縮液の比重と沸点上昇温度から前記式(3)によ
り濃縮液中の懸濁物質の濃度を推定する。From the temperature of the concentrate and the temperature of the generated steam during the concentration circulation, the boiling point rise temperature is determined by the above equation (4), and the suspension in the concentrate is calculated by the above equation (3) from the measured specific gravity of the concentrate and the boiling point rise temperature. Estimate the concentration of suspended matter.
【0026】もし、懸濁物質の濃度が5wt%未満とな
ったときは、濃縮液排出ラインにサイクロンセパレータ
ーに代表される固液分離設備を設け、懸濁物質を回収し
て返送する。また懸濁物質濃度が25wt%を超える
と、懸濁物質が配管に閉塞する懸念があるため濃縮倍率
を下げるような運転をする。このような方法により種晶
(懸濁物質)の濃度を調整することにより、蒸発濃縮器
2内でのスケールの発生を防止することができる。If the concentration of the suspended solids becomes less than 5 wt%, a solid-liquid separation facility typified by a cyclone separator is provided in the concentrated liquid discharge line to collect and return the suspended solids. If the concentration of the suspended solids exceeds 25 wt%, there is a concern that the suspended solids may be clogged in the pipes, so that the operation is performed to reduce the concentration ratio. By adjusting the concentration of the seed crystal (suspension substance) by such a method, generation of scale in the evaporator 2 can be prevented.
【0027】図2は、濃縮液中の懸濁物質濃度を自動で
推定する場合のフロー図であるが、図中共通する装置
は、共通の番号を付し説明を省略する。比重計14、濃
縮液温度計6、発生蒸気温度計7で計測した電気信号
(点線)を入力信号とし、予め求めて記憶した相関式
(1),(2),(3)と式(4)に比重、濃縮液温度
および発生蒸気温度の値を代入し、懸濁物質濃度推定装
置16で演算することにより、濃縮液中の懸濁物質濃度
をリアルタイムで推定することができる。推定した懸濁
物質濃度を、5wt%〜25wt%の範囲に維持するこ
とにより、スケーリングの発生を防止することができ
る。FIG. 2 is a flow chart in the case of automatically estimating the concentration of the suspended substance in the concentrated liquid. In the figure, the same devices are denoted by the same reference numerals and description thereof is omitted. The electric signals (dotted lines) measured by the specific gravity meter 14, the concentrated liquid thermometer 6, and the generated steam thermometer 7 are used as input signals, and the correlation formulas (1), (2), (3) and (4) obtained and stored in advance are used. The values of the specific gravity, the temperature of the concentrated solution, and the temperature of the generated steam are substituted in the above), and the suspended substance concentration estimating device 16 calculates the suspended substance concentration in the concentrated liquid in real time. By maintaining the estimated suspended solid concentration in the range of 5 wt% to 25 wt%, the occurrence of scaling can be prevented.
【0028】[0028]
【実施例】以下実施例により本発明を詳細に説明する
が、本発明はこれらの実施例により限定されるものでは
ない。The present invention will be described in detail with reference to the following examples, but the present invention is not limited to these examples.
【0029】実施例1 実施例における、蒸発濃縮試験は表1に示した脱硫排水
を、−500mmHgおよび約70℃の濃縮条件で蒸発
濃縮し、約12倍まで濃縮運転を実施した。Example 1 In the evaporative concentration test in the examples, the desulfurization effluent shown in Table 1 was evaporated and concentrated under the conditions of -500 mmHg and about 70 ° C., and the concentration operation was performed to about 12 times.
【0030】[0030]
【表1】 [Table 1]
【0031】表1の脱硫排水を約12倍まで濃縮する過
程において、濃縮液の全蒸発残留物と比重をJIS K
0102に基づいて適宜測定し、両者の相関関係を求め
たところ、以下の通りであった。なお比重計はコリオリ
式密度計(桜エンドレス社製(型番63FS25)を使
用した。In the process of concentrating the desulfurized effluent of Table 1 to about 12 times, the total evaporation residue and specific gravity of the concentrated liquid were determined according to JIS K
Appropriately determined on the basis of 0102, it was determined both correlation relationships were as follows. The specific gravity meter used was a Coriolis type densitometer (Sakura Endless, model number 63FS25).
【0032】 全蒸発残留物(wt%)=160×(比重−1) 同様に濃縮過程において沸点上昇温度と溶解性蒸発残留
物をJIS K0102に基づいて適宜測定し、両者の
関係を求めたところ相関式は以下の通りであった。Total evaporation residue (wt%) = 160 × (specific gravity-1) Similarly, in the concentration process, the boiling point increase temperature and the soluble evaporation residue were appropriately measured based on JIS K0102, and the relationship between the two was determined. The correlation equation was as follows.
【0033】 溶解性蒸発残留物(wt%)=8×沸点上昇温度(℃) 従って、懸濁物質の濃度は、以下の式で表される。Soluble evaporation residue (wt%) = 8 × boiling point temperature (° C.) Accordingly, the concentration of the suspended substance is represented by the following equation.
【0034】 懸濁物質濃度(wt%)=160×(比重−1)−8×沸点上昇温度(℃) =160×(比重−1)−8×(溶液温度(℃)− 発生蒸気温度(℃)) 上記式により、蒸発濃縮中の濃縮液の比重、濃縮液温
度、発生蒸気温度の測定値から懸濁物質の濃度を推定し
た。また、その時の濃縮液をJIS K0102に基づ
いて分析し、懸濁物質の濃度を分析した。懸濁物質濃度
の推定値(横軸、演算値)と分析値(縦軸、分析値)の
結果を図3に示した。Suspended substance concentration (wt%) = 160 × (specific gravity−1) −8 × boiling point rise temperature (° C.) = 160 × (specific gravity−1) −8 × (solution temperature (° C.) − Evolved steam temperature ( ° C)) According to the above equation, the concentration of the suspended substance was estimated from the measured values of the specific gravity of the concentrated solution during the evaporation concentration, the concentrated solution temperature, and the generated steam temperature. Further, the concentrated liquid at that time was analyzed based on JIS K0102, and the concentration of the suspended substance was analyzed. FIG. 3 shows the results of the estimated value (horizontal axis, calculated value) and the analytical value (vertical axis, analytical value) of the concentration of the suspended solids.
【0035】図3に示した結果から明らかなように、本
発明方法による懸濁物質の濃度の推定値は、懸濁物質の
分析値とよく相関していた。As is clear from the results shown in FIG. 3, the estimated value of the concentration of the suspended substance according to the method of the present invention correlated well with the analytical value of the suspended substance.
【0036】[0036]
【発明の効果】本発明方法により、溶解性蒸発残留物お
よび懸濁物質を含む溶液の懸濁物質濃度を正確かつリア
ルタイムに推定することができる。According to the method of the present invention, the concentration of a suspended substance in a solution containing a soluble evaporation residue and a suspended substance can be estimated accurately and in real time.
【0037】本発明方法により、溶解性蒸発残留物およ
び懸濁物質を含む脱硫排水の蒸発濃縮する際に、スケー
リング防止の重要な因子である種晶(懸濁物質)の濃度
をリアルタイムに測定することができ、スケーリングを
容易に防止することができる。According to the method of the present invention, when evaporating and concentrating desulfurization effluent containing soluble evaporation residues and suspended solids, seed crystals (suspended solids) which are important factors for preventing scaling are removed . The concentration can be measured in real time, and scaling can be easily prevented.
【0038】また、本発明方法は、自動化が容易であ
り、脱硫排水の蒸発濃縮の自動運転が可能となる。Further, the method of the present invention is easy to automate, and enables automatic operation of evaporative concentration of desulfurization wastewater.
【図1】脱硫排水を蒸発濃縮する際の濃縮液中の懸濁物
質濃度を推定するためのフロー図。FIG. 1 is a flow chart for estimating the concentration of suspended solids in a concentrated liquid when evaporating and condensing desulfurization wastewater.
【図2】脱硫排水を蒸発濃縮する際の濃縮液中の懸濁物
質濃度を自動で推定するためのフロー図。FIG. 2 is a flowchart for automatically estimating the concentration of suspended solids in a concentrated liquid when evaporating and condensing desulfurization wastewater.
【図3】実施例1における濃縮液中の懸濁物質濃度の本
発明による推定値と分析値の関係を示すグラフ。FIG. 3 is a graph showing a relationship between an estimated value according to the present invention and an analytical value of the concentration of a suspended substance in a concentrated solution in Example 1.
1 pH調整槽 2 蒸発濃縮器 3 コンデンサ 4 濃縮液タンク 5 pH調整薬品槽 6 循環液温度 7 発生蒸気温度計 8 pH調整薬品注入ポンプ 9 排水供給ポンプ 10 濃縮液循環ポンプ 11 真空ポンプ 12 凝縮水ポンプ 13 蒸気ドレンポンプ 14 比重計 15 切り換え弁 16 懸濁物質濃度推定装置 aa 排水供給ライン bb 加熱蒸気ライン cc 冷却水入口ライン dd 冷却水出口ライン DESCRIPTION OF SYMBOLS 1 pH adjustment tank 2 Evaporation concentrator 3 Condenser 4 Concentrated liquid tank 5 pH adjusted chemical tank 6 Circulating fluid temperature 7 Generated steam thermometer 8 pH adjusted chemical injection pump 9 Drainage supply pump 10 Concentrated liquid circulation pump 11 Vacuum pump 12 Condensed water pump 13 Steam drain pump 14 Densitometer 15 Switching valve 16 Suspended substance concentration estimating device aa Wastewater supply line bb Heating steam line cc Cooling water inlet line dd Cooling water outlet line
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.7 識別記号 FI C02F 1/04 (72)発明者 高橋 英紀 東京都文京区本郷5丁目5番16号 オル ガノ株式会社内 (72)発明者 伊藤 智章 東京都文京区本郷5丁目5番16号 オル ガノ株式会社内 (56)参考文献 特開 昭51−51997(JP,A) (58)調査した分野(Int.Cl.7,DB名) G01N 25/10 B01D 1/00 B01D 53/34 ZAB B01D 53/50 B01D 53/77 C02F 1/04 ──────────────────────────────────────────────────の Continued on the front page (51) Int.Cl. 7 Identification symbol FI C02F 1/04 (72) Inventor Hideki Takahashi 5-5-1-16 Hongo, Bunkyo-ku, Tokyo Organo Corporation (72) Inventor Tomoaki Ito 5-5-16 Hongo, Bunkyo-ku, Tokyo Organo Corporation (56) References JP-A-51-51997 (JP, A) (58) Fields investigated (Int. Cl. 7 , DB name) G01N 25/10 B01D 1/00 B01D 53/34 ZAB B01D 53/50 B01D 53/77 C02F 1/04
Claims (4)
溶液の懸濁物質濃度を推定する方法において、予め全蒸
発残留物と溶液の比重との相関式(1) 全蒸発残留物(wt%)=f(比重) …… (1) を求め、さらに溶解性蒸発残留物と沸点上昇温度との相
関式(2) 溶解性蒸発残留物(wt%)=f(沸点上昇温度) …… (2) を求め、溶解性蒸発残留物および懸濁物質を含む溶液の
比重と沸点上昇温度を測定し、測定した比重と沸点上昇
温度を式(3) 懸濁物質(wt%)=f(比重)−f(沸点上昇温度) …… (3) に代入して演算することを特徴とする溶解性蒸発残留物
および懸濁物質を含む溶液の懸濁物質濃度の推定方法。In a method for estimating the concentration of a suspended substance in a solution containing a soluble evaporation residue and a suspended substance, a correlation equation between the total evaporation residue and the specific gravity of the solution (1) %) = F (specific gravity) (1) is obtained, and a correlation equation between the soluble evaporation residue and the boiling point rise temperature (2) Soluble evaporation residue (wt%) = f (boiling point rise temperature) (2) is determined, the specific gravity and the boiling point rise temperature of the solution containing the soluble evaporation residue and the suspended substance are measured, and the measured specific gravity and the boiling point rise temperature are expressed by the following equation (3): suspended substance (wt%) = f ( Specific gravity) -f (boiling point rise temperature) A method for estimating the concentration of a suspended substance in a solution containing a soluble evaporation residue and a suspended substance, which is calculated by substituting into (3).
気温度を測定して、式(4) 沸点上昇温度(℃)=溶液温度(℃)−発生蒸気温度(℃) …… (4) により求めることを特徴とする請求項1に記載の懸濁物
質濃度の推定方法。2. The boiling point rise temperature, the solution temperature and the generated steam temperature are measured, and the following equation (4): Boiling point rise temperature (° C.) = Solution temperature (° C.) − Generated steam temperature (° C.) (4) The method for estimating the concentration of a suspended substance according to claim 1, wherein the estimation is performed.
溶液が、溶解性蒸発残留物および懸濁物質を含む脱硫排
水である請求項1または請求項2に記載の懸濁物質濃度
の推定方法。3. A solution comprising a soluble evaporation residue and suspended solids, soluble evaporation residue and suspended matter estimation of suspended matter concentration according to claim 1 or claim 2 is desulfurized effluent containing Method.
脱硫排水を循環して蒸発濃縮する方法において、請求項
1記載の方法により蒸発濃縮液中の懸濁物質濃度を推定
し、懸濁物質濃度を5wt%〜25wt%に維持するこ
とを特徴とする脱硫排水の蒸発濃縮方法。4. A method of circulating desulfurization wastewater containing a soluble evaporation residue and a suspended substance and evaporating and concentrating the suspension, estimating the concentration of the suspended substance in the evaporative concentrated liquid by the method according to claim 1, A method for evaporating and condensing desulfurization wastewater, wherein the substance concentration is maintained at 5 wt% to 25 wt%.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP09075131A JP3133272B2 (en) | 1997-03-27 | 1997-03-27 | Method for estimating suspended solids concentration and evaporating and concentrating desulfurization wastewater |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP09075131A JP3133272B2 (en) | 1997-03-27 | 1997-03-27 | Method for estimating suspended solids concentration and evaporating and concentrating desulfurization wastewater |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH10267871A JPH10267871A (en) | 1998-10-09 |
| JP3133272B2 true JP3133272B2 (en) | 2001-02-05 |
Family
ID=13567342
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|---|---|---|---|
| JP09075131A Expired - Fee Related JP3133272B2 (en) | 1997-03-27 | 1997-03-27 | Method for estimating suspended solids concentration and evaporating and concentrating desulfurization wastewater |
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Families Citing this family (2)
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|---|---|---|---|---|
| AU2002953236A0 (en) * | 2002-12-10 | 2003-01-02 | Mario Panuccio | Process for operating a water treatment plant |
| CN105954313B (en) * | 2016-05-30 | 2018-09-07 | 珠海格力电器股份有限公司 | Method and system for determining boiling point temperature |
-
1997
- 1997-03-27 JP JP09075131A patent/JP3133272B2/en not_active Expired - Fee Related
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| Publication number | Publication date |
|---|---|
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