JPH06130049A - Method for sequential analysis of concentration of carbonate and sulfite in liquid - Google Patents
Method for sequential analysis of concentration of carbonate and sulfite in liquidInfo
- Publication number
- JPH06130049A JPH06130049A JP4281437A JP28143792A JPH06130049A JP H06130049 A JPH06130049 A JP H06130049A JP 4281437 A JP4281437 A JP 4281437A JP 28143792 A JP28143792 A JP 28143792A JP H06130049 A JPH06130049 A JP H06130049A
- Authority
- JP
- Japan
- Prior art keywords
- liquid
- concentration
- sulfite
- carbonate
- reaction vessel
- 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.)
- Granted
Links
Landscapes
- Investigating Or Analyzing Non-Biological Materials By The Use Of Chemical Means (AREA)
- Treating Waste Gases (AREA)
Abstract
Description
【0001】[0001]
【産業上の利用分野】本発明はカルシウム塩をアルカリ
源とする湿式排煙脱硫装置における吸収液中の炭酸塩及
び亜硫酸塩濃度を逐次分析測定する方法に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for sequentially analyzing and measuring the concentrations of carbonate and sulfite in an absorbing solution in a wet flue gas desulfurization apparatus using a calcium salt as an alkali source.
【0002】[0002]
【従来の技術】従来、液中の炭酸塩及び亜硫酸塩の濃度
の連続測定装置では炭酸塩及び亜硫酸塩を含有する液を
外気と遮断した攪拌式連続反応容器内で塩酸もしくは硫
酸と反応させ、下記反応によって炭酸塩及び亜硫酸塩を
各々CO2 及びSO2 となし、 (塩酸を用いた場合) CaCO3 +2HCl → CaCl2 +CO2 ↑+H2 O ・・・(1) CaSO3 +2HCl → CaCl2 +SO2 ↑+H2 O ・・・(2) (硫酸を用いた場合) CaCO3 +H2 SO4 → CaSO4 +CO2 ↑+H2 O ・・・(3) CaSO3 +H2 SO4 → CaSO2 +SO2 ↑+H2 O ・・・(4) これを反応液中に空気を吹込み抜気し、抜気ガス中のC
O2 及びSO2 の量を検出して、液中に含まれる炭酸塩
及び亜硫酸塩の濃度を演算によって算出している。2. Description of the Related Art Conventionally, in a continuous measuring device for the concentration of carbonate and sulfite in a liquid, a liquid containing carbonate and sulfite is reacted with hydrochloric acid or sulfuric acid in an agitated continuous reaction vessel which is isolated from the outside air, The following reaction forms carbonate and sulfite into CO 2 and SO 2 , respectively (when hydrochloric acid is used): CaCO 3 + 2HCl → CaCl 2 + CO 2 ↑ + H 2 O (1) CaSO 3 + 2HCl → CaCl 2 + SO 2 ↑ + H 2 O ・ ・ ・ (2) (when using sulfuric acid) CaCO 3 + H 2 SO 4 → CaSO 4 + CO 2 ↑ + H 2 O ・ ・ ・ (3) CaSO 3 + H 2 SO 4 → CaSO 2 + SO 2 ↑ + H 2 O (4) Air is blown into the reaction solution to degas it, and C in the degassed gas
The amounts of O 2 and SO 2 are detected, and the concentrations of carbonate and sulfite contained in the liquid are calculated.
【0003】従来法について図2に基づき説明する。図
2において、炭酸塩及び亜硫酸塩を含有する供試液Aは
定量ポンプ1で採取され、反応容器5内の滞留液6の温
度が所定温度となるように同滞留液6の温度を温度検出
器4で検出し、温度調節計3からの信号で熱源制御され
ている加熱器2を経由して昇温後反応容器5へ供給され
る。The conventional method will be described with reference to FIG. In FIG. 2, the sample solution A containing carbonate and sulfite is sampled by the metering pump 1, and the temperature of the retained liquid 6 in the reaction vessel 5 is adjusted to a predetermined temperature by a temperature detector. The temperature is detected in step 4, and the temperature is supplied to the reaction vessel 5 after heating via the heater 2 whose heat source is controlled by the signal from the temperature controller 3.
【0004】同反応容器5の滞留液6はpH検出器14
でpHを検出し、pH調節計15からの信号で微量ポン
プ12を制御し、硫酸(もしくは塩酸)Cを反応容器5
へ注入して所要pHとなるようにpH制御されており、
さらにその際、反応式(3)〜(4)(もしくは(1)
〜(2))に従って発生するCO2 及びSO2 を円滑に
抜気するために、流量調節計11で所要流量に制御され
ている空気Bの一部もしくは分配弁22を操作して流量
指示計17並びに空気吹込管8を介して滞留液6中に吹
込むと共に、同反応容器5内の滞留液6はシール材9を
介してモータ10で駆動する攪拌機7によって攪拌され
ている。The stagnant liquid 6 in the reaction vessel 5 is a pH detector 14
PH is detected by the pH controller 15, the micro pump 12 is controlled by a signal from the pH controller 15, and sulfuric acid (or hydrochloric acid) C is added to the reaction vessel 5.
PH is controlled by injecting into
Further, at that time, reaction formulas (3) to (4) (or (1)
- (2) in order to smoothly degassing of CO 2 and SO 2 generated in accordance), flow indicator by operating portion or a dispensing valve 22 of the air B, which is controlled to a required flow rate at a flow rate adjusting meter 11 The stagnant liquid 6 is blown into the stagnant liquid 6 via 17 and an air blowing pipe 8, and the stagnant liquid 6 in the reaction container 5 is stirred by a stirrer 7 driven by a motor 10 via a sealing material 9.
【0005】次に定量ポンプ1からの試料液Aの供給に
よる滞留液6の液量の増加分はオーバーフロー管23か
ら液封器13に排出され、同液封器13では反応容器5
内のCO2 及びSO2 含有ガスEがオーバーフロー液に
同伴して洩れ出さないように反応容器5の内圧に打ち勝
つだけの液深となるようにオーバーフロー管23の先端
は液封器13内の液中に浸漬されており、同液封器13
に流入するオーバーフロー液の余剰液量は廃液Dとなっ
て排出される。Next, an increase in the amount of the stagnant liquid 6 due to the supply of the sample liquid A from the metering pump 1 is discharged from the overflow pipe 23 to the liquid sealer 13, and in the liquid sealer 13, the reaction container 5 is discharged.
The tip of the overflow pipe 23 is at the tip of the liquid in the liquid sealer 13 so that the gas E containing CO 2 and SO 2 in the inside of the overflow container 23 does not leak along with the overflow liquid so that the internal pressure of the reaction container 5 is overcome. It is submerged in the same liquid sealer 13
The surplus liquid amount of the overflow liquid flowing into is discharged as waste liquid D.
【0006】反応式(3)〜(4)(もしくは(1)〜
(2))に従って発生したCO2 もしくはSO2 並びに
空気吹込管8からの空気と蒸発水分との混合ガスEは反
応容器5をバイパスしている空気16と合流したのち排
気Fとして放出されるが、その排気Fの一部は除湿器2
4で含有している水分をドレンHとして除去されたのち
空気ポンプ18で吸引され、CO2 分析計19並びにS
O2 分析計25に送られ、同CO2 分析計19並びにS
O2 分析計25で各々CO2 濃度並びにSO2濃度が測
定されてのち排気Gとして放出される。CO2 分析計1
9並びにSO2分析計25での各々の測定信号は液中の
炭酸塩濃度並びに亜硫酸塩濃度を算出するための炭酸塩
濃度演算器20並びに亜硫酸塩濃度演算器26に送ら
れ、液採取流量信号*2及び空気流量信号*1の各値と
共に演算処理され液中の炭酸塩及び亜硫酸塩の濃度を次
式で算出し、炭酸塩濃度は濃度指示計21でまた亜硫酸
塩濃度は濃度指示計27で各々指示されている。 炭酸塩濃度〔モル/リットル〕= x1 ×Q/(100−x1 −x2 )×22.4×L ・・・(5) 亜硫酸塩濃度〔モル/リットル〕= x2 ×Q/(100−x1 −x2 )×22.4×L ・・・(6) x1 :CO2 濃度〔容量%〕 x2 :SO2 濃度〔容量%〕 Q :吹込み用と混合用各空気の合計流量〔Nリットル
/分〕 L :液採取流量〔リットル/分〕Reaction formulas (3) to (4) (or (1) to
The CO 2 or SO 2 generated according to (2) and the mixed gas E of the air and the evaporated water from the air blowing pipe 8 joins the air 16 bypassing the reaction vessel 5 and is then discharged as the exhaust gas F. , Part of the exhaust F is the dehumidifier 2
The water contained in 4 is removed as drain H and then sucked by the air pump 18, and the CO 2 analyzer 19 and S
It is sent to the O 2 analyzer 25, and the same CO 2 analyzer 19 and S
The CO 2 concentration and the SO 2 concentration are measured by the O 2 analyzer 25, and the exhaust gas G is discharged. CO 2 analyzer 1
9 and the respective measurement signals of the SO 2 analyzer 25 are sent to a carbonate concentration calculator 20 and a sulfite concentration calculator 26 for calculating the carbonate concentration and the sulfite concentration in the liquid, and a liquid sampling flow rate signal. * 2 and the air flow rate signal * 1 are calculated and the concentration of carbonate and sulfite in the liquid is calculated by the following formula. The carbonate concentration is measured by the concentration indicator 21 and the sulfite concentration is measured by the concentration indicator 27. Each is instructed by. Carbonate concentration [mol / l] = x 1 × Q / (100 -x 1 -x 2) × 22.4 × L ··· (5) sulfite concentration [mol / l] = x 2 × Q / ( 100-x 1 -x 2 ) × 22.4 × L (6) x 1 : CO 2 concentration [volume%] x 2 : SO 2 concentration [volume%] Q: Air for injection and mixture Total flow rate [N liter / minute] L: Liquid sampling flow rate [liter / minute]
【0007】[0007]
【発明が解決しようとする課題】本発明で検出対象とし
ている湿式排煙脱硫装置における吸収液中の炭酸塩は炭
酸カルシウムであり、その溶解度は小さいため通常固体
として液中に懸濁している。また亜硫酸塩は亜硫酸カル
シウムとして存在するが、最近主流となっているいわゆ
るタンク酸化式プロセスにおいては循環液タンク内に直
接空気を吹込んで100%近い酸化率を得ているため、
その濃度は固体を析出するまでには高くなく、溶液中の
みにイオンとして存在する場合が大部分である。かかる
吸収液を検出対象とした場合には、従来法の如く吸収液
を直接攪拌式連続反応容器に供給する方式を採用する場
合には以下の問題を有していた。The carbonate in the absorbing liquid in the wet flue gas desulfurization apparatus to be detected in the present invention is calcium carbonate, and since its solubility is low, it is usually suspended in the liquid as a solid. Sulfite exists as calcium sulfite, but in the so-called tank oxidation process that has recently become the mainstream, air is blown directly into the circulating fluid tank to obtain an oxidation rate close to 100%.
The concentration is not high enough to precipitate a solid, and in most cases, it exists as ions only in the solution. When such an absorbent is to be detected, the following problems have been encountered when the method of directly supplying the absorbent to the continuous stirring type continuous reaction vessel as in the conventional method is adopted.
【0008】すなわち、前述の如く吸収液中の亜硫酸塩
濃度と炭酸塩濃度レベルが大幅に異なるため、検出精度
を向上させるためには通常低濃度の側、すなわち亜硫酸
塩の濃度レベルに合わせて攪拌式連続反応容器に供給す
る吸収液量を調節させる必要があった。すなわち、吸収
液量が少ないと前記(6)式で示したx2 :SO2 濃度
〔容量%〕が検出下限以下となり、SO2 濃度に換言す
ると吸収液中の亜硫酸塩濃度の精度よい測定が不可能と
なってしまう。そこで供給液量を増大させて充分な精度
を維持できるようにする必要があるが、この際には以下
の不都合が生じる。That is, as described above, since the sulfite concentration and the carbonate concentration level in the absorbing liquid are greatly different, in order to improve the detection accuracy, the concentration is usually low, that is, the stirring is performed according to the sulfite concentration level. It was necessary to adjust the amount of absorbing liquid supplied to the continuous reaction vessel. That is, when the amount of the absorbing liquid is small, the x 2 : SO 2 concentration [volume%] shown in the above formula (6) becomes lower than the lower limit of detection, and in other words, the SO 2 concentration can be measured accurately. It becomes impossible. Therefore, it is necessary to increase the supply amount of liquid so that sufficient accuracy can be maintained, but in this case, the following inconvenience occurs.
【0009】すなわち、連続式反応容器中には硫酸(も
しくは塩酸)を注入して前記(1)、(2)式(もしく
は(3)、(4)式)の反応を起こしてCO2 及びSO
2 を発生させるのであるが、この際吸収液中亜硫酸塩濃
度に比較して著しく高い濃度で存在する炭酸カルシウム
濃度の中和によって大量の硫酸(もしくは塩酸)が消費
されてしまうという不都合が生じる。That is, sulfuric acid (or hydrochloric acid) is injected into a continuous reaction vessel to cause the reactions of the above formulas (1) and (2) (or (3) and (4)) to produce CO 2 and SO 2.
Although to generate a 2, disadvantageously large amount of sulfuric acid by the neutralization of the calcium carbonate concentration present in significantly higher concentrations in comparison with the case sulfite concentration in the absorbing liquid (or hydrochloric acid) is consumed occurs.
【0010】本発明は上記技術水準に鑑み、上記低濃度
の亜硫酸塩検出のために大量の酸が消費される従来の欠
点を解消しうる液中の炭酸塩及び亜硫酸塩の濃度を逐次
分析する方法を提供しようとするものである。In view of the above-mentioned state of the art, the present invention sequentially analyzes the concentrations of carbonate and sulfite in a liquid which can solve the conventional drawback that a large amount of acid is consumed for detecting low concentration of sulfite. It is intended to provide a method.
【0011】[0011]
【課題を解決するための手段】本発明は炭酸塩は主とし
て固体として存在し、亜硫酸塩は溶液として存在するこ
とに注目し、炭酸塩を固液分離後、ろ液を低濃度の亜硫
酸塩に見合った充分な量を攪拌式連続反応容器へ供給し
て酸によりSO2 を発生させることにより、精度よくし
かも酸の消費を極力低減できることを見いだし、この知
見に基づいて本発明を完成するに至った。In the present invention, it is noted that carbonate exists mainly as a solid, and sulfite exists as a solution. After solid-liquid separation of carbonate, the filtrate is converted into a low-concentration sulfite. It was found that the consumption of the acid can be reduced with high precision by supplying a sufficient amount to the stirring type continuous reaction vessel to generate SO 2 by the acid, and the present invention was completed based on this finding. It was
【0012】すなわち、本発明は炭酸塩及び亜硫酸塩を
含有する液中の炭酸塩及び亜硫酸塩濃度を連続検出する
に際し、該液を連続定量採取し、これを外気とは遮断さ
れた攪拌式連続反応容器へ供給し、同反応容器内液は温
度を50℃以上とするとともに硫酸もしくは塩酸を空気
と混合して同反応容器内液中に吹き込み、液中の炭酸塩
及び亜硫酸塩と酸との反応によって生成するCO2 とS
O2 を同反応容器外へ抜き出し、同抜き出しガス中に含
まれるCO2 及びSO2 濃度と前記液採取流量及び吹込
み空気流量の各値から液中の炭酸塩濃度及び亜硫酸塩濃
度を求める方法において、該液を固液分離してろ液のみ
を前記攪拌式連続反応容器に供給して前記手段によって
亜硫酸塩濃度を求める操作と、該液を固液分離すること
なく前記攪拌式連続反応容器に供給して前記手段によっ
て炭酸塩濃度を求める操作を交互に切換えて行なうこと
を特徴とする液中の炭酸塩及び亜硫酸塩の濃度を逐次分
析する方法である。That is, according to the present invention, when the concentration of carbonate and sulfite in a liquid containing carbonate and sulfite is continuously detected, the liquid is continuously and quantitatively sampled, and this is continuously stirred with the outside air. The solution in the reaction vessel is heated to 50 ° C. or higher and sulfuric acid or hydrochloric acid is mixed with air and blown into the solution in the reaction vessel to remove the carbonate and sulfite in the solution and the acid. CO 2 and S produced by the reaction
A method of extracting O 2 from the same reaction vessel, and obtaining the carbonate concentration and sulfite concentration in the liquid from the CO 2 and SO 2 concentrations contained in the extracted gas, and the liquid sampling flow rate and the blown air flow rate. In, the liquid is subjected to solid-liquid separation, only the filtrate is supplied to the stirring type continuous reaction vessel to determine the sulfite concentration by the means, and the liquid is separated into the stirring type continuous reaction vessel without solid-liquid separation. It is a method for sequentially analyzing the concentrations of carbonate and sulfite in a liquid, which is characterized in that the operations of supplying and determining the carbonate concentration by the above means are alternately switched.
【0013】[0013]
【作用】以下本発明の構成と作用を図1により更に詳細
に説明する。図1は本発明の一実施態様例の説明図であ
り、図1についての説明では図2に示した従来法と異な
る点についてのみ説明し、従来法に準ずる構成の説明は
割愛する。The structure and operation of the present invention will be described in more detail with reference to FIG. FIG. 1 is an explanatory diagram of an embodiment of the present invention. In the description of FIG. 1, only the points different from the conventional method shown in FIG. 2 will be described, and the description of the configuration according to the conventional method will be omitted.
【0014】図1において供試液Aはポンプ28より液
体サイクロン29を経てオーバーフロー、すなわちろ液
が切換弁30に供給されるラインと、ポンプ31を経て
切換弁30に直接送られラインの2つに分割される。液
体サイクロン29のアンダーフローはライン32を経て
系外に排出される。切換弁30に供給された供試液は流
量制御弁33を経て加熱器2を経由して昇温後反応器5
へ供給される。ここで切換弁30はタイマー機構をもつ
調節器34よりの信号*3により一定時間間隔で切換え
られ前記2区分された供試液が交互に流量制御弁33を
経て反応容器5へ供給される機能を有する。また信号*
3より流量制御弁33の流量調節計35の液量設定値が
切換えられる。具体的には液体サイクロン29のオーバ
ーフロー液が流量制御弁33を流れる場合には流量設定
値を増大させ、ポンプ31を経た供試液が流れる場合と
は流量設定値を低下させる。In FIG. 1, the test solution A is overflowed from the pump 28 through the hydrocyclone 29, that is, the filtrate is supplied to the switching valve 30 and the line is directly sent to the switching valve 30 via the pump 31 into two lines. Will be divided. The underflow of the liquid cyclone 29 is discharged to the outside of the system through the line 32. The test solution supplied to the switching valve 30 passes through the flow rate control valve 33, the heater 2, and the post-heating reactor 5
Is supplied to. Here, the switching valve 30 has a function of being switched at a constant time interval by a signal * 3 from a controller 34 having a timer mechanism so that the two divided test solutions are alternately supplied to the reaction vessel 5 via the flow control valve 33. Have. Signal *
3, the liquid amount set value of the flow rate controller 35 of the flow rate control valve 33 is switched. Specifically, when the overflow liquid of the hydrocyclone 29 flows through the flow rate control valve 33, the flow rate setting value is increased, and when the sample liquid that has passed through the pump 31 flows, the flow rate setting value is decreased.
【0015】流量調節計35からの流量信号*4は炭酸
塩濃度演算器20並びに亜硫酸塩濃度演算器26に送ら
れ、空気流量信号*1の値と共に前記(5)及び(6)
式により演算処理される。なお、切換弁30の切換え間
隔は供試液中の炭酸塩及び亜硫酸塩の検出時間間隔要求
に応じて調節器34のタイマー機構により任意に設定で
きる。The flow rate signal * 4 from the flow rate controller 35 is sent to the carbonate concentration calculator 20 and the sulfite concentration calculator 26, and together with the value of the air flow rate signal * 1, the above (5) and (6).
It is calculated by an expression. The switching interval of the switching valve 30 can be arbitrarily set by the timer mechanism of the controller 34 according to the detection time interval requirement of the carbonate and the sulfite in the sample liquid.
【0016】[0016]
【実施例】図1に示した本発明の方法により、調製した
標準試料を測定したところ以下の結果を得た。 平均濃度〔モル/リットル〕 変動係数 (10点平均) (標準偏差/平均値) 〇炭酸塩 0.051 0.020 〇亜硫酸塩 0.0021 0.047 〇塩酸供給量 2.03 〔ミリリットル/分〕 たゞし、炭酸塩、亜硫酸塩濃度は各々ポンプ31及び液
体サイクロン29を経て供試料を採取した場合の値を示
す。EXAMPLE A standard sample prepared by the method of the present invention shown in FIG. 1 was measured and the following results were obtained. Average concentration [mol / liter] Coefficient of variation (10-point average) (standard deviation / average) 〇 Carbonate 0.051 0.020 〇 Sulfite 0.0021 0.047 〇 Hydrochloric acid supply 2.03 [mL / min] However, the carbonate and sulfite concentrations show the values when a sample is taken through the pump 31 and the liquid cyclone 29, respectively.
【0017】ここで標準試料の組成及び他の条件は次の
とおりであった。 〇標準試料組成 : 炭酸カルシウム 0.051
〔モル/リットル〕 亜硫酸カルシウム 0.0022〔モル/リットル〕 (亜硫酸はすべて液相に存在していた。) 〇供試料の採取量: ポンプ31を経る供試料採取量 0.12〔リットル/分〕 液体サイクロン29を経る供試料採取量 1.0〔リットル/分〕 〇吹込み空気流量: 7〔Nリットル/分〕 〇全空気流量 : 20〔Nリットル/分〕 〇反応温度設定 : 75〔℃〕 〇反応pH設定 : 2.5〔−〕 〇流路切換え時間間隔: 5〔分〕 〇供給酸の種類 : 塩酸 〇酸の濃度 : 6規定The composition of the standard sample and other conditions were as follows. 〇 Standard sample composition: Calcium carbonate 0.051
[Mole / liter] Calcium sulfite 0.0022 [mol / liter] (Sulfurous acid was all present in the liquid phase.) 〇 Amount of sample collected: Amount of sample collected through the pump 31 0.12 [liter / min. ] Amount of sample to be sampled through the hydrocyclone 29 1.0 [liter / minute] ○ Flow rate of blown air: 7 [Nliter / minute] ○ Total air flow rate: 20 [Nliter / minute] ○ Reaction temperature setting: 75 [ ℃] 〇 Reaction pH setting: 2.5 [-] 〇 Flow path switching time interval: 5 [minutes] 〇 Type of supplied acid: hydrochloric acid 〇 Concentration of acid: 6 normal
【0018】〔比較例〕実施例と同一の装置にてポンプ
31のみを経て供試料を採取するようタイマーを調節
し、実施例と同一の標準試料を測定したところ以下の結
果を得た。 平均濃度〔モル/リットル〕 変動係数 (10点平均) (標準偏差/平均値) 〇炭酸塩 0.051 0.024 〇亜硫酸塩 0.0017 0.24 〇塩酸供給量 2.26 〔ミリリットル/分〕 供試料の採取量、吹込み空気流量、全空気流量、反応温
度設定、反応pH設定、供給酸の種類、酸の濃度は実施
例と同一である。[Comparative Example] A timer was adjusted so as to collect a sample through the pump 31 only in the same apparatus as in Example, and the same standard sample as in Example was measured, and the following results were obtained. Average concentration [mol / liter] Coefficient of variation (10-point average) (standard deviation / average) 〇 Carbonate 0.051 0.024 〇 Sulfite 0.0017 0.24 〇 Hydrochloric acid supply 2.26 [mL / min] The amount of sample to be collected, the flow rate of blown air, the total flow rate of air, the reaction temperature setting, the reaction pH setting, the type of the supplied acid, and the acid concentration are the same as those in the examples.
【0019】実施例と比較例を比べると炭酸塩の濃度に
ついては平均濃度、変動係数ともほとんど同じことか
ら、分析精度に差はないが、亜硫酸塩濃度については、
比較例の平均値は真値と大きな差があり、かつ変動係数
も大きいことから、本発明による分析精度の向上が明ら
かである。また、消費された塩酸量は本発明の方法が比
較例に比べて少ない。Comparing the examples and the comparative examples, there is no difference in analysis accuracy because the average concentration and the coefficient of variation of the carbonate concentration are almost the same, but regarding the sulfite concentration,
Since the average value of the comparative example has a large difference from the true value and the coefficient of variation is also large, it is clear that the analysis accuracy is improved by the present invention. Moreover, the amount of hydrochloric acid consumed is smaller in the method of the present invention than in the comparative example.
【0020】[0020]
【発明の効果】本発明によれば、供試液中に溶存してい
る極く低濃度の亜硫酸塩濃度を従来法に比較して高精度
でしかも酸の消費量を増大することなく分析することが
可能となる。INDUSTRIAL APPLICABILITY According to the present invention, it is possible to analyze the extremely low concentration of sulfite dissolved in a test solution with high accuracy as compared with the conventional method and without increasing the amount of acid consumption. Is possible.
【図1】本発明の一実施例の説明図。FIG. 1 is an explanatory diagram of an embodiment of the present invention.
【図2】従来のカルシウム塩をアルカリ源とする湿式排
煙脱硫装置における吸収液中の炭酸塩及び亜硫酸塩濃度
を分析する方法の一態様の説明図。FIG. 2 is an explanatory view of one embodiment of a method for analyzing the concentration of carbonate and sulfite in an absorbing solution in a conventional wet flue gas desulfurization apparatus using a calcium salt as an alkali source.
Claims (1)
酸塩及び亜硫酸塩濃度を連続検出するに際し、該液を連
続定量採取し、これを外気とは遮断された攪拌式連続反
応容器へ供給し、同反応容器内液は温度を50℃以上と
するとともに硫酸もしくは塩酸を空気と混合して同反応
容器内液中に吹き込み、液中の炭酸塩及び亜硫酸塩と酸
との反応によって生成するCO2 とSO2 を同反応容器
外へ抜き出し、同抜き出しガス中に含まれるCO2 及び
SO2 濃度と前記液採取流量及び吹込み空気流量の各値
から液中の炭酸塩濃度及び亜硫酸塩濃度を求める方法に
おいて、該液を固液分離してろ液のみを前記攪拌式連続
反応容器に供給して前記手段によって亜硫酸塩濃度を求
める操作と、該液を固液分離することなく前記攪拌式連
続反応容器に供給して前記手段によって炭酸塩濃度を求
める操作を交互に切換えて行なうことを特徴とする液中
の炭酸塩及び亜硫酸塩の濃度を逐次分析する方法。1. When continuously detecting the concentrations of carbonate and sulfite in a liquid containing carbonate and sulfite, the liquid is continuously and quantitatively sampled, and the liquid is transferred to an agitated continuous reaction vessel which is shielded from the outside air. The temperature of the liquid in the reaction vessel is raised to 50 ° C. or higher, and sulfuric acid or hydrochloric acid is mixed with air and blown into the liquid in the reaction vessel, which is produced by the reaction between the carbonate and sulfite in the liquid and the acid. CO 2 and SO 2 are extracted from the reaction vessel, and the concentration of CO 2 and SO 2 contained in the extracted gas and the respective values of the liquid sampling flow rate and the blowing air flow rate are used to determine the concentration of carbonate and sulfite in the liquid. In the method for determining the concentration, the liquid is subjected to solid-liquid separation, and only the filtrate is supplied to the stirring type continuous reaction vessel to determine the sulfite concentration by the means, and the stirring type is used without solid-liquid separation of the liquid. Supply to continuous reaction vessel How to sequentially analyze the concentration of carbonate and sulfite in the liquid, characterized in that performing an operation for obtaining the carbonate concentration by serial means alternately switched.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP4281437A JP3015604B2 (en) | 1992-10-20 | 1992-10-20 | Method for sequential analysis of carbonate and sulfite concentrations in liquid |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP4281437A JP3015604B2 (en) | 1992-10-20 | 1992-10-20 | Method for sequential analysis of carbonate and sulfite concentrations in liquid |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH06130049A true JPH06130049A (en) | 1994-05-13 |
JP3015604B2 JP3015604B2 (en) | 2000-03-06 |
Family
ID=17639161
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP4281437A Expired - Fee Related JP3015604B2 (en) | 1992-10-20 | 1992-10-20 | Method for sequential analysis of carbonate and sulfite concentrations in liquid |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP3015604B2 (en) |
-
1992
- 1992-10-20 JP JP4281437A patent/JP3015604B2/en not_active Expired - Fee Related
Also Published As
Publication number | Publication date |
---|---|
JP3015604B2 (en) | 2000-03-06 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
US6010664A (en) | Oxidation detection for sulfite/sulfate systems | |
US5601784A (en) | On-line control and monitoring system for wet lime/limestone flue gas desulfurization process | |
JP2004093465A (en) | Weight measurement type slurry densitometer and measuring method | |
US4677077A (en) | Method for measuring the concentration of CaCO3 in a slurry | |
US4683211A (en) | Method for measuring the concentration of CaCO3 in a slurry | |
JPH033906B2 (en) | ||
CA2518581A1 (en) | Hydrogen sulfide monitoring system | |
JPH06130049A (en) | Method for sequential analysis of concentration of carbonate and sulfite in liquid | |
JPH11118782A (en) | Ammonia nitrogen measuring device | |
JP4996895B2 (en) | Calcium carbonate concentration measuring method, measuring device and calcium carbonate concentration control device | |
US4683210A (en) | Method for measuring concentrations of CaCO3 and CaSO3 in a slurry | |
EP0466303B1 (en) | Method and system for continuously monitoring and controlling a process stream for dechlorination residual | |
JP3120525B2 (en) | Anaerobic digester monitoring device | |
JP3172745B2 (en) | Method for measuring peroxodisulfuric acid in wastewater | |
Jones et al. | Experimental and theoretical studies of solid solution formation in lime and limestone SO2 scrubbers | |
JP2005024357A (en) | Automatic measuring device for water processing agent concentration | |
JPS58162852A (en) | Automatic titration analyzer | |
JPS60154157A (en) | Method for measuring continuously concentration of caco3 and concentration of caso3 in slurry | |
JP2794758B2 (en) | Silver production equipment with low palladium content | |
JPH0733157Y2 (en) | Carbonate analyzer | |
JPS634139B2 (en) | ||
JPS60222133A (en) | Method for supplying acid in continuous analysis of concentration of carbonate and sulfite in liquid | |
JP3120532B2 (en) | Control device for anaerobic digester monitor | |
JP2000131306A (en) | Method and instrument for measuring carbonate concentration in slurry | |
SU852797A1 (en) | Method of sulfuric acid production process control |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
A01 | Written decision to grant a patent or to grant a registration (utility model) |
Free format text: JAPANESE INTERMEDIATE CODE: A01 Effective date: 19991124 |
|
LAPS | Cancellation because of no payment of annual fees |