JPS6057399B2 - Demineralizer group control device - Google Patents
Demineralizer group control deviceInfo
- Publication number
- JPS6057399B2 JPS6057399B2 JP53130468A JP13046878A JPS6057399B2 JP S6057399 B2 JPS6057399 B2 JP S6057399B2 JP 53130468 A JP53130468 A JP 53130468A JP 13046878 A JP13046878 A JP 13046878A JP S6057399 B2 JPS6057399 B2 JP S6057399B2
- Authority
- JP
- Japan
- Prior art keywords
- demineralizer
- control device
- ion
- throughput
- switching valve
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired
Links
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E30/00—Energy generation of nuclear origin
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E30/00—Energy generation of nuclear origin
- Y02E30/30—Nuclear fission reactors
Landscapes
- Treatment Of Water By Ion Exchange (AREA)
Description
【発明の詳細な説明】
本発明は脱塩器群制御装置に係り、原子力発電所の復水
脱塩器における再生作業の周期を制御するものに関する
。DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a demineralizer group control device, and more particularly, to one that controls the cycle of regeneration work in a condensate demineralizer in a nuclear power plant.
原子力発電所で使用する水は、特に高純度に維持する必
要があり、通常においては復水脱塩器によつて入口水中
の固形物及びイオンを除去している。Water used in nuclear power plants must be maintained at a particularly high level of purity, and solids and ions in the inlet water are usually removed by a condensate demineralizer.
復水脱塩器は複数台設置されているが、使用中その内の
一台は待機状態としている。待機状態のものは、使用中
のものの逆流或いは再生を行うとき切替えて連続運転を
するためのものである。There are multiple condensate demineralizers installed, but one of them is on standby while it is in use. The one in the standby state is for continuous operation by switching when backflowing or regenerating the one in use.
逆流は脱塩器に固形物が付着して出入口間の差圧が上昇
した場合に水によつて洗浄する作業である。また、再生
は脱塩器のイオン処理量が多くなり、その性能が低下し
た場合に薬品によつて行う作業であり、逆流工程も行わ
れる。ここで、イオン処理量は入口及び出口のイオン濃
度差ど脱塩器通過水量の積で求める場合が多い。再生は
硫酸、苛性ソーダで行われ、再生廃液として液体廃棄物
処理系に送られる。再生廃液は硫酸ナトリウムを多量に
含んでいるため、主に濃縮器で処理されている。発電所
の運転状態が一定に保持されていれば、復水脱塩器入口
液のイオン濃度は一定であるが、例えば、復水器より冷
却用の海水が混入される等が起ると入口液のイオン濃度
は上昇する。Backflow is the process of cleaning the demineralizer with water when solid matter adheres to it and the differential pressure between the inlet and outlet increases. In addition, regeneration is an operation performed using chemicals when the amount of ions processed by the demineralizer increases and its performance deteriorates, and a backflow process is also performed. Here, the ion throughput is often determined by the product of the ion concentration difference at the inlet and outlet and the amount of water passing through the demineralizer. Regeneration is performed with sulfuric acid and caustic soda, and the regeneration waste liquid is sent to the liquid waste treatment system. Recycled waste liquid contains a large amount of sodium sulfate, so it is mainly treated with a concentrator. If the operating conditions of the power plant are maintained constant, the ion concentration of the condensate demineralizer inlet liquid will be constant, but if, for example, seawater for cooling is mixed in from the condenser, the inlet The ion concentration of the liquid increases.
この場合、脱塩器のイオン処理量が多くなり、再生周期
が短かくなり、さらに、待機脱塩器の運転方法を考慮し
ないと再生が2台以上重なることが考えられる。液体廃
棄物処理系の濃縮器は処理速度が通常小さく、廃棄の発
生が重なると、多大な労力を要するばかりか、再生作業
を数日間遅延させなければならない可能性がある。In this case, the ion throughput of the demineralizer increases, the regeneration cycle becomes short, and furthermore, unless the operating method of the standby demineralizers is taken into account, it is conceivable that two or more demineralizers will be regenerated at the same time. Concentrators in liquid waste treatment systems typically have low throughput rates, and the combined waste generation not only requires significant effort, but may also delay the reclamation operation by several days.
これを避けるためには、濃縮器の処理能力を増大する方
法がある。この方法は、これに伴う加熱用ボイラー容量
、設置面積の増加があり、しかも、平常運転時での利用
率の低下があるため、大幅な増加は困難である。本発明
は以上の点を鑑みなされたもので、脱塩器の運用を制御
して再生が2台以上重ならないようにさせ、再生作業を
円滑に行うとともに、液体廃棄物処理系を効率良く運転
てきる脱塩器制御装置を提供することを目的とする。本
発明は、同一発明者の発明1脱塩器群制御装置J(特願
昭49−93421(特公昭槃−47228号公報))
において、海水混入時等の運用方法に改良を加えたもの
である。脱塩器入口液のイオン濃度が高くなると、再生
作業が主となり逆洗作業は行われなくなる。この場合、
゛イオン処理量が脱塩器群で2番目に多い脱塩器を待機
させて再生を遅らせ、再生作業が2台以上重ならないよ
うにしたものである。以下、本発明を添付図面に示した
実施例に基づいて説明する。To avoid this, there is a method of increasing the throughput of the concentrator. This method requires an increase in the heating boiler capacity and installation area, and also reduces the utilization rate during normal operation, making it difficult to achieve a significant increase. The present invention was developed in view of the above points, and it controls the operation of desalination equipment to prevent regeneration from occurring in two or more units at the same time, so that the regeneration work can be carried out smoothly, and the liquid waste treatment system can be operated efficiently. The purpose of the present invention is to provide a demineralizer control device that can perform the following steps. The present invention is based on Invention 1 Demineralizer group control device J (Japanese Patent Application No. 49-93421 (Japanese Patent Publication No. 47228)) by the same inventor.
This is an improvement to the operation method when seawater gets mixed in. When the ion concentration of the demineralizer inlet liquid becomes high, regeneration work becomes the main activity and backwashing work is no longer performed. in this case,
``The demineralizer with the second highest ion throughput in the demineralizer group is put on standby to delay regeneration, so that regeneration work does not overlap with two or more units. Hereinafter, the present invention will be described based on embodiments shown in the accompanying drawings.
第1図は原子力発電所の主蒸気復水系統及び再生廃液処
理系の構成を示している。Figure 1 shows the configuration of the main steam condensate system and regenerated waste liquid treatment system of a nuclear power plant.
前者の系統は原子炉1、蒸気タービン2、復水器4、復
水脱塩器5,6,1、給水ポンプ8を順次連結して構成
している。後者の系統は、樹脂再生装置9、廃液収集タ
ンク10、及び廃液処理装置12を順次連結して構成し
ている。さらに、前者の系統には切替弁14,15,1
6、流量計17,18,19、電導度計20,21,2
2,23,24,25が接続されている。これら、切替
弁、流量計、電導度計には、制御装置26が信号線27
,28,・・38によつて接続されている。上記電導度
計20,21,22,23,24,25は復水脱塩器5
,6,7の入口側及び出口側の電導度を6検出するもの
である。流量計17,18,19は処理流量を検出する
ものである。制御装置26は、以上の検出結果を総合し
て計算することによつて復水脱塩器5,6,7の状態を
記憶し、イオン処理量が2番目に多い脱塩器を待機させ
るよう.に運転制御するものである。この制御装置26
の出力によつて、切替弁14,15,16は切替制御さ
れる。上記蒸気タービン2には発電機3が連結されてい
る。つぎに、制御装置26を第2図を基に説明す−る。The former system is constructed by sequentially connecting a nuclear reactor 1, a steam turbine 2, a condenser 4, a condensate demineralizer 5, 6, 1, and a feed water pump 8. The latter system is constructed by sequentially connecting a resin regenerating device 9, a waste liquid collection tank 10, and a waste liquid processing device 12. Furthermore, the former system has switching valves 14, 15, 1.
6, Flowmeter 17, 18, 19, Conductivity meter 20, 21, 2
2, 23, 24, and 25 are connected. The control device 26 connects the signal line 27 to the switching valve, flowmeter, and conductivity meter.
, 28, . . . 38. The conductivity meters 20, 21, 22, 23, 24, 25 are the condensate demineralizer 5
, 6 and 7 are used to detect the electrical conductivity on the inlet side and outlet side. Flowmeters 17, 18, and 19 are for detecting the processing flow rate. The control device 26 stores the states of the condensate demineralizers 5, 6, and 7 by comprehensively calculating the above detection results, and puts the demineralizer with the second highest ion throughput on standby. .. It controls the operation. This control device 26
The switching valves 14, 15, and 16 are controlled by the output. A generator 3 is connected to the steam turbine 2. Next, the control device 26 will be explained based on FIG. 2.
制御装置26は、タイマ装置40,41、イオン処理量
計算装置42、演算装置43,44,・・・・49、弁
切替装置50から構成されている。イオン処理量計算装
置42には信号線30,31,・ ・・38が接続され
、弁切替装置50には信号線27,28,29が接続さ
れている。演算装置43,46には端子51,52及び
接続線53,54が接続されている。端子51,52は
再生開始イオン処理量設定値及び海水等混入判定用設定
値である。つぎに作用を説明する。The control device 26 includes timer devices 40, 41, an ion throughput calculation device 42, arithmetic devices 43, 44, . . . 49, and a valve switching device 50. Signal lines 30, 31, . . . , 38 are connected to the ion throughput calculation device 42, and signal lines 27, 28, 29 are connected to the valve switching device 50. Terminals 51, 52 and connection lines 53, 54 are connected to the computing devices 43, 46. Terminals 51 and 52 are a regeneration start ion processing amount set value and a set value for seawater contamination determination. Next, the effect will be explained.
原子炉1で発生した蒸気は、蒸気タービン2に動力を付
与し、その後復水器4で液化され、この・水は脱塩器5
,6,7で浄化される。The steam generated in the reactor 1 powers a steam turbine 2 and is then liquefied in a condenser 4, and this water is passed through a desalination machine 5.
, 6, 7.
その後、水は原子炉1に給水される。原子炉で使用する
水は特に高純度に浄化する必要があり、復水脱塩器5,
6,7では水中のイオン並びにクラッド主にFe2O3
を除去するが、所定の性能を維持させるため、脱塩器5
,6,7内の樹脂を適宜樹脂再生装置9に送り、逆洗或
いは再生作業を行つている。海水混入等でイオン処理量
が急激に増加すると、再生作業が主になる。この時の廃
液は廃液収集タンク10に集められ、次いで廃液処理装
置12で浄化された後復水貯蔵タンク13に送られる。
つぎに、制御装置26の作用を説明する。第2図は制御
装置26の構成、第3図は動作手順を示したものであり
、制御用計算機で実行する場合はサブプログラムとなる
。流量計17,18,19及び電導度計20,21,・
・・・・25の各出力は信号線30,31,・38を介
してイオ7処理量計算装置42に入力される。Water is then supplied to the reactor 1. Water used in nuclear reactors must be purified to a particularly high degree of purity, and condensate desalination equipment 5,
In 6 and 7, ions and cladding in water are mainly Fe2O3.
However, in order to maintain the specified performance, the demineralizer 5
, 6, 7 is sent to a resin regenerating device 9 as appropriate for backwashing or regeneration work. When the amount of ions to be processed increases rapidly due to seawater contamination, etc., regeneration work becomes the main task. The waste liquid at this time is collected in a waste liquid collection tank 10, then purified in a waste liquid treatment device 12, and then sent to a condensate storage tank 13.
Next, the operation of the control device 26 will be explained. FIG. 2 shows the configuration of the control device 26, and FIG. 3 shows the operating procedure, which becomes a subprogram when executed by a control computer. Flow meters 17, 18, 19 and conductivity meters 20, 21, .
. . 25 are input to the Io7 throughput calculation device 42 via signal lines 30, 31, and 38.
ここでは、各脱塩器の入口側と出口側の電導度の差に流
量を乗じ、過去の値に加算してイオン処理量の積算値と
する。処理したイオン量を炭酸カルシウムに換算する場
合には第4図の関係で補正する。これは第3図において
ステップAである。計算結果は、一定周期で信号を発生
するタイマ40よりの信号で動作するスイッチ41を介
して、演算装置43,44,45に送られる。演算器4
3では再生開始時刻を次のようにして予測し、信号線5
3に出力する。第5図において現時点をPOとし、脱塩
器1,■のイオン処理量がQl,Q2であるとする。P
1で海水混入等が起つたとし、この状態が持続すれば、
再生開始時刻はt1後の時点P2となる。計算機を用い
る場合、過去数日間のデータを統計的に処理して求める
ことができる。これはステップBである。演算装置44
では、各脱塩器のイオン処理量の変化分を計算し、これ
の平均値;を求める。これはステップCである。演算装
置46では、設定値E<5iとを比較し、次のように判
定する。これはステップDである。b<ξ 平常運転、
海水混入等なし
i≧ξ 海水混入等が考えられる。Here, the difference in conductivity between the inlet and outlet sides of each demineralizer is multiplied by the flow rate and added to the past value to obtain the integrated value of the ion throughput. When converting the amount of treated ions into calcium carbonate, the relationship shown in FIG. 4 is used to correct the amount. This is step A in FIG. The calculation results are sent to arithmetic units 43, 44, and 45 via a switch 41 operated by a signal from a timer 40 that generates a signal at a constant cycle. Arithmetic unit 4
In 3, the playback start time is predicted as follows, and the signal line 5 is
Output to 3. In FIG. 5, it is assumed that the current time is PO, and the ion throughputs of the demineralizers 1 and 2 are Ql and Q2. P
Suppose seawater contamination occurs in step 1, and if this situation continues,
The reproduction start time is time point P2 after t1. When using a computer, it can be calculated by statistically processing data from the past few days. This is step B. Arithmetic device 44
Now, calculate the changes in the ion throughput of each desalter and find the average value. This is step C. The arithmetic unit 46 compares the set value E<5i and makes the following determination. This is step D. b<ξ Normal operation,
No seawater contamination, etc. i≧ξ Seawater contamination, etc. is possible.
i<εの場合は脱塩器の運用はそのままとするように信
号を54に送り、i≧εの場合は演算装置48,49に
信号を送る。If i<ε, a signal is sent to 54 to leave the demineralizer operating as is, and if i≧ε, a signal is sent to arithmetic units 48, 49.
演算装置48では電導度と流量より海水等の漏洩量を計
算し、信号線−53に出力する。これはステップEであ
る。演算装置45ではイオン処理量が脱塩器群で2番目
に多い脱塩器を選択し、これはステップFである、演算
装置49で待機中か否かを判定する。これはステップG
である。待機中の場合は信号線54に出力し脱塩器は運
用はそのままとするが、使用中の場合は弁切替装置50
に信号を送り、待機状態にさせる。これはステップHで
ある。なお、脱塩器の待機状態は、各脱塩器の流量をチ
ェックすることにより行うことができ、演算装置47で
行う。つぎに、4台の復水脱塩器1,■,■,■の運用
を制御した場合の一例を第6図について説明する。The arithmetic unit 48 calculates the leakage amount of seawater or the like from the conductivity and flow rate and outputs it to the signal line -53. This is step E. The arithmetic unit 45 selects the demineralizer with the second largest ion throughput in the demineralizer group, and in step F, the arithmetic unit 49 determines whether or not it is on standby. This is step G
It is. When it is on standby, it is output to the signal line 54 and the demineralizer continues to operate, but when it is in use, it is output to the signal line 54, but when it is in use, it is output to the signal line 54.
sends a signal to put it on standby. This is step H. Note that the standby state of the demineralizers can be established by checking the flow rate of each demineralizer, and is performed by the arithmetic unit 47. Next, an example of controlling the operation of the four condensate demineralizers 1, 1, 2, and 2 will be described with reference to FIG.
図において、TAは再生に要する時間、T8は本発明の
動作を行わせる周期で、具体的には第2図のタイマ40
がスイッチ41に信号を発する周期である。今、復水脱
塩器1,■,■,■の運転初期において、脱塩器1,■
,■のイオン処理量がほぼ等しい場合を考える。Bl,
B2,B3の点では、イオン処理量が2番目の脱塩器を
待機させている。A1の点では、脱塩器1のイオン処理
量が再生開始量Rtに達し、再生を行なうため待機状態
となる。さらに、B,の点ではイオン処理量が2番目の
脱塩器を待機させる。以上の操作を繰返すことによつて
、従来A1点付近で脱塩器1,■,■,を集中的に再出
しなければならなかつた状態が、Al,〜,A8のよう
に分散される。In the figure, TA is the time required for reproduction, and T8 is the period at which the operation of the present invention is performed. Specifically, the timer 40 in FIG.
is the period at which a signal is issued to the switch 41. Now, in the initial stage of operation of condensate demineralizer 1,■,■,■,
Consider the case where the ion throughput of , ■ is almost equal. Bl,
At points B2 and B3, the demineralizer with the second highest ion throughput is on standby. At point A1, the ion processing amount of the demineralizer 1 reaches the regeneration start amount Rt, and the demineralizer 1 enters a standby state for regeneration. Furthermore, at point B, the desalter with the second highest ion throughput is placed on standby. By repeating the above operations, the conventional situation in which the demineralizers 1, 1, 2, had to be intensively re-extracted near the A1 point is dispersed to Al, to A8.
第6図の特性においては逆洗作業が示されていないが、
海水混入時等には再生作業が主体となり、再生作業時に
は逆洗工程も含まれているためである。なお、実施例中
復水脱塩器5,6,7は3個であるが、発電所によつて
この数は変化しても、その数に応じて本発明は実施でき
る。Although backwashing is not shown in the characteristics shown in Figure 6,
This is because when seawater is mixed in, the main activity is regeneration work, and the regeneration work also includes a backwashing process. In the embodiment, there are three condensate demineralizers 5, 6, and 7, but even if this number changes depending on the power plant, the present invention can be implemented according to the number.
本発明によれば、海水混入時等においても脱塩器の再生
時期が分散されるため、再生作業を円滑に行うことがで
きる。According to the present invention, the regeneration timing of the desalter is dispersed even when seawater is mixed in, so the regeneration work can be carried out smoothly.
しかも、樹脂再生時期が把握できるため、事前に受入れ
準備を行う等、運転を効率的に行うことができる。Furthermore, since the timing of resin regeneration can be determined, operations can be carried out efficiently, such as by preparing for acceptance in advance.
第1図は原子力発電所の系統を示すブロック図、第2図
は本発明の制御装置を示すブロック図、第3図はその動
作を示す説明図、第4図、第5図は各演算装置の特性説
明図、第6図は制御装門置の運転特性説明図である。
5・・・・・・復水脱塩器、14・・・・・・切替弁、
17・・・・・流量計、20・・・・・電導度計、23
・・・・・・電導度計、26・・・・・制御装置、42
・・・・・・イオン処理量計算装置、43〜49・・・
・・・演算装置、50・・・・・・弁切替装フ置。Fig. 1 is a block diagram showing the system of a nuclear power plant, Fig. 2 is a block diagram showing the control device of the present invention, Fig. 3 is an explanatory diagram showing its operation, and Figs. 4 and 5 are each arithmetic device. FIG. 6 is an explanatory diagram of the operating characteristics of the control device. 5...Condensate demineralizer, 14...Switching valve,
17...Flowmeter, 20...Conductivity meter, 23
... Conductivity meter, 26 ... Control device, 42
...Ion throughput calculation device, 43-49...
... Arithmetic device, 50 ... Valve switching device.
Claims (1)
に設けられ、その使用を切替える切替弁と、各脱塩器及
び切替弁の間に設けられた電導度計及び流量計と、各脱
塩器の出口部に設けられた電導度計と、上記電導度計、
流量計の各出力を演算し、その演算出力によつてイオン
処理量が2番目に多い脱塩器を待機させるように上記切
替弁を切替制御する制御装置とを具備したことを特徴と
する脱塩器群制御装置。 2 特許請求の範囲第1項記載の装置において、制御装
置を、各脱塩器の入口及び出口液の電導度並びに流量に
より、各脱塩器のイオン処理量を計算する装置と、単位
時間当りのイオン処理増加量を求め、設定量と比較する
装置と、イオン処理量が脱塩器群で2番目に多い脱塩器
を待機状態にさせるための装置とから構成したことを特
徴とする脱塩器群制御装置。[Scope of Claims] 1. A plurality of condensate demineralizers, a switching valve provided at the inlet of each demineralizer to switch its use, and a switching valve provided between each demineralizer and the switching valve. a conductivity meter and a flow meter, a conductivity meter provided at the outlet of each demineralizer, and the conductivity meter,
The demineralizer is characterized by comprising a control device that calculates each output of the flowmeter and switches and controls the switching valve so that the demineralizer with the second highest ion throughput is placed on standby based on the calculated output. Salt ware group control device. 2. In the apparatus according to claim 1, the control device comprises a device that calculates the ion throughput of each demineralizer based on the conductivity and flow rate of the inlet and outlet liquids of each demineralizer, and a device that calculates the ion throughput of each demineralizer per unit time. The demineralizer is characterized in that it is comprised of a device for determining the increased amount of ion processing and comparing it with a set amount, and a device for placing the demineralizer with the second highest ion throughput in the demineralizer group in a standby state. Salt ware group control device.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP53130468A JPS6057399B2 (en) | 1978-10-25 | 1978-10-25 | Demineralizer group control device |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP53130468A JPS6057399B2 (en) | 1978-10-25 | 1978-10-25 | Demineralizer group control device |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5556882A JPS5556882A (en) | 1980-04-26 |
| JPS6057399B2 true JPS6057399B2 (en) | 1985-12-14 |
Family
ID=15034955
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP53130468A Expired JPS6057399B2 (en) | 1978-10-25 | 1978-10-25 | Demineralizer group control device |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS6057399B2 (en) |
Families Citing this family (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US4469602A (en) * | 1982-08-27 | 1984-09-04 | Autotrol Corporation | Microcomputer controlled demand/scheduled water softener having automatic resin bed sensing |
| JPS59170796A (en) * | 1983-03-18 | 1984-09-27 | 株式会社東芝 | Condensed water clean-up device |
| JPS6312393A (en) * | 1986-07-02 | 1988-01-19 | Toshiba Corp | Automatic operation control device for condensate desalting column |
| JPS63153499A (en) * | 1986-12-18 | 1988-06-25 | 株式会社日立製作所 | Nuclear reactor coolant purification system |
-
1978
- 1978-10-25 JP JP53130468A patent/JPS6057399B2/en not_active Expired
Also Published As
| Publication number | Publication date |
|---|---|
| JPS5556882A (en) | 1980-04-26 |
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