JP2005144213A - Method and system for controlling adhesion and growth of marine organism - Google Patents

Method and system for controlling adhesion and growth of marine organism Download PDF

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JP2005144213A
JP2005144213A JP2003380967A JP2003380967A JP2005144213A JP 2005144213 A JP2005144213 A JP 2005144213A JP 2003380967 A JP2003380967 A JP 2003380967A JP 2003380967 A JP2003380967 A JP 2003380967A JP 2005144213 A JP2005144213 A JP 2005144213A
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seawater
cooling water
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JP4102736B2 (en
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Kenji Tokumasa
賢治 徳政
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Chugoku Electric Power Co Inc
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Abstract

<P>PROBLEM TO BE SOLVED: To control the concentration of chlorine in seawater discharged into sea at low level while effectively controlling the adhesion and growth of marine organisms, such as shellfishes, in a cooling water system with a chlorine-based chemical when cooling target equipment with seawater. <P>SOLUTION: A cooling water system 28 comprises water intake passages 20A, 20B for supplying cooling water (seawater) to steam condensers 18A, 18B, a discharge passage 22 for discharging the seawater, having passed through the steam condensers 18A, 18B, to sea, and an LNG vaporizer passage 27 for circulating a part of the seawater discharged from the discharge passage 22 to an LNG vaporizer 17. Chemical injection parts 32A-32C are installed in the vicinities of the water intake ports of the water intake passages 20A, 20B and the inlet of the LNG vaporizer passage 27. The chemical injection ports 32A-32C are switched sequentially to inject a sodium hypochlorite solution into the passages sequentially. <P>COPYRIGHT: (C)2005,JPO&NCIPI

Description

本発明は海水を用いて復水器等の装置を冷却するための冷却水系統内において海洋生物の付着及び成長を抑制するための方法及びシステムに関する。   The present invention relates to a method and system for suppressing the attachment and growth of marine organisms in a cooling water system for cooling an apparatus such as a condenser using seawater.

冷却水として海水を利用する火力発電所においては、海から海水を取り入れて復水器に供給する取水路や、復水器を通った海水を海へ放出するための放水路の内部に貝等の海洋生物が付着し易い。かかる海洋生物の付着量が多くなると、冷却水の流路が塞がれて冷却性能が低下するなどの不具合を招くおそれがある。そこで、従来より、例えば、特許文献1や特許文献2に開示されるように、次亜塩素酸ナトリウム溶液や二酸化塩素等の塩素系薬剤を冷却水の流路に注入することにより、流路おいて海洋生物の付着及び成長を抑制することが行われている。
特開平7−265867号公報 特開平11−37666号公報
In thermal power plants that use seawater as cooling water, shells, etc. are placed inside the intake channel that takes seawater from the ocean and supplies it to the condenser, and the discharge channel that releases the seawater that has passed through the condenser to the ocean. The marine life is easy to adhere. When the adhesion amount of such marine organisms increases, there is a risk of causing problems such as blocking the cooling water flow path and lowering the cooling performance. Therefore, conventionally, as disclosed in, for example, Patent Document 1 and Patent Document 2, a chlorine-based chemical such as a sodium hypochlorite solution or chlorine dioxide is injected into the flow path of the cooling water, thereby In order to prevent the attachment and growth of marine organisms.
JP-A-7-265867 Japanese Patent Laid-Open No. 11-37666

上述のように、火力発電所において冷却水として利用された後の海水は海へ放出されるが、環境保全のために、海への放出水に含まれる塩素濃度(残留塩素濃度)は一定の協定値以下であることが要求される。したがって、海洋生物を除去するための塩素系薬剤の注入量も、上記の要求を満足できるように制限しなければならず、この制限の範囲内で十分な除去効果を得ることは容易でない。   As mentioned above, seawater after being used as cooling water in thermal power plants is released to the sea, but for environmental conservation, the chlorine concentration (residual chlorine concentration) contained in the discharged water to the sea is constant. It is required to be below the agreed value. Therefore, the injection amount of the chlorinated chemical for removing marine organisms must be limited so as to satisfy the above requirements, and it is not easy to obtain a sufficient removal effect within the limits.

本発明は上記の点に鑑みてなされたものであり、冷却対象設備を海水により冷却するにあたり、冷却水系統を構成する流路において海洋生物の付着及び成長を塩素系薬剤で効果的に抑制しつつ、海へ放出される海水中の塩素濃度を低く抑えることができるようにすることを目的とする。   The present invention has been made in view of the above points, and when cooling a facility to be cooled with seawater, adhesion and growth of marine organisms are effectively suppressed with a chlorine-based chemical in a flow path constituting the cooling water system. On the other hand, an object is to make it possible to keep the chlorine concentration in the seawater released to the sea low.

上記の目的を達成するため、請求項1に記載された発明は、冷却水として海から海水を取り入れて冷却対象設備に供給し、この冷却対象設備を通った後の海水を海へ放出するための冷却水系統内において海洋生物の付着及び成長を抑制する方法であって、
前記冷却水系統を構成する複数の流路のうち少なくとも2つの流路に、夫々、塩素系薬剤を注入するための薬剤注入部を設け、それら薬剤注入部の中から順次切り替えて選択した薬剤注入部により該当する流路内へ塩素系薬剤を注入することを特徴とする。
In order to achieve the above object, the invention described in claim 1 is for taking seawater from the sea as cooling water and supplying it to the facility to be cooled, and discharging the seawater after passing through the facility to be cooled to the sea. A method for suppressing the attachment and growth of marine organisms in the cooling water system of
A drug injection unit for injecting a chlorine-based drug is provided in at least two of the plurality of channels constituting the cooling water system, and the drug injection selected by sequentially switching from among the drug injection units It is characterized by injecting a chlorinated chemical into the corresponding flow path by the part.

本発明によれば、複数の冷却水流路に夫々薬剤注入部を設け、それら薬剤注入部の中から順次切り替えて選択した薬剤注入部により、該当する流路内へ塩素系薬剤を注入する。このため、塩素系薬剤が注入された流路では高い残留塩素濃度を得て海洋生物の付着及び成長を効果的に抑制できる。また、塩素系薬剤が注入される流路は順次切り替えられるので、各流路に付着した海洋生物は順次除去されることになる。一方、海へ放出される海水には、塩素系薬剤が注入されない流路の海水も含まれるため塩素成分は希釈され、その残留塩素濃度は低く抑えられる。このように、本発明によれば、海へ放出される海水の残留塩素濃度を低く抑えながら、冷却水系統内において海洋生物の付着及び成長を効果的に抑制することができる。   According to the present invention, a drug injection part is provided in each of the plurality of cooling water flow paths, and a chlorinated drug is injected into the corresponding flow path by the drug injection part selected by switching sequentially from among the drug injection parts. For this reason, high residual chlorine concentration can be obtained in the flow path into which the chlorine-based chemical is injected, and marine organisms can be effectively prevented from attaching and growing. Moreover, since the flow paths into which the chlorinated chemicals are injected are sequentially switched, marine organisms attached to the respective flow paths are sequentially removed. On the other hand, the seawater released into the sea includes seawater in a channel into which no chlorine-based chemicals are injected, so that the chlorine component is diluted and the residual chlorine concentration is kept low. Thus, according to the present invention, it is possible to effectively suppress the adhesion and growth of marine organisms in the cooling water system while keeping the residual chlorine concentration of seawater released to the sea low.

また、請求項2に記載された発明は、請求項1記載の方法において、前記塩素系薬剤として次亜塩素酸ナトリウムを注入することを特徴とする。   The invention described in claim 2 is characterized in that, in the method according to claim 1, sodium hypochlorite is injected as the chlorinated drug.

また、請求項3に記載された発明は、請求項1又は2記載の方法において、前記冷却水系統は、海から取り込んだ海水を複数の前記冷却対象設備へ夫々送るための複数の取水路と、前記冷却対象設備を通過した海水を海へ放出するための放水路とを含んでおり、
前記薬剤注入部を前記複数の取水路の夫々の取水口近傍に設けることを特徴とする。
The invention described in claim 3 is the method according to claim 1 or 2, wherein the cooling water system includes a plurality of intake passages for sending seawater taken from the sea to the plurality of facilities to be cooled, respectively. And a water discharge channel for discharging seawater that has passed through the facility to be cooled to the sea,
The medicine injection part is provided in the vicinity of each water intake port of the plurality of water intake channels.

また、請求項4に記載された発明は、請求項1〜3のうち何れか1項記載の方法において、前記冷却対象設備は、液化天然ガス(LNG)火力発電所に設けられた設備であり、前記放水路を流れる海水をLNG気化器に循環させるためのLNG気化器流路が設けられており、
少なくとも一つの前記薬剤注入部を前記LNG気化器流路に設けることを特徴とする。
Moreover, the invention described in claim 4 is the method according to any one of claims 1 to 3, wherein the cooling target facility is a facility provided in a liquefied natural gas (LNG) thermal power plant. , An LNG vaporizer flow path for circulating the seawater flowing through the discharge channel to the LNG vaporizer is provided,
At least one of the drug injection portions is provided in the LNG vaporizer flow path.

また、請求項5に記載された発明は、冷却水として海から海水を取り入れて冷却対象設備に供給し、この冷却対象設備を通った後の海水を海へ放出するための冷却水系統内において海洋生物の付着及び成長を抑制するシステムであって、
前記冷却水系統を構成する複数の流路のうち少なくとも2つの流路に設けられた、塩素系薬剤を注入するための薬剤注入部と、
前記複数の薬剤注入部の中から順次切り替えて選択した薬剤注入部により該当する流路内へ塩素系薬剤を注入させる制御手段と、を備えることを特徴とする。
Moreover, in the cooling water system for taking in the seawater as the cooling water from the sea and supplying it to the equipment to be cooled, and discharging the seawater after passing through the equipment to be cooled to the sea. A system for suppressing the attachment and growth of marine organisms,
A drug injection part for injecting a chlorine-based drug, provided in at least two channels among the plurality of channels constituting the cooling water system;
Control means for injecting a chlorine-based drug into the corresponding flow path by a drug injection unit selected by switching sequentially from the plurality of drug injection units.

本発明によれば、海へ放出される海水の残留塩素濃度を低く抑えながら、冷却水系統内において貝等の海洋生物の付着及び成長を効果的に抑制することができる。   ADVANTAGE OF THE INVENTION According to this invention, adhesion and growth of marine organisms, such as a shellfish, can be effectively suppressed within a cooling water system | strain, suppressing the residual chlorine density | concentration of the seawater discharge | released to the sea low.

図1は、本発明の一実施形態に係わる火力発電所10の概略平面図である。同図に示す如く、火力発電所10は海2に臨む敷地に建設されている。火力発電所10には、例えば燃料貯蔵設備12、LNGタンク14、発電設備16、LNG気化器17等の各種設備が設けられている。本実施形態では、発電設備16に設けられた2系統の復水器18A,18Bを海水で冷却するものとしており、海2から海水を取り込んで復水器18A,18Bへ夫々供給するための取水路20A,20Bと、復水器18A,18Bを通った海水を海2へ放出するための放水路22とが設置されている。海水は取水路20A,20Bの先端の取水口24A,24Bから取リ込まれ、取水路20A,20Bを流れて夫々復水器18A,18Bを通った後、両系統に共通の放水路22を通って、その先端の放水口26から海2へ放出される。   FIG. 1 is a schematic plan view of a thermal power plant 10 according to an embodiment of the present invention. As shown in the figure, the thermal power plant 10 is constructed on a site facing the sea 2. The thermal power plant 10 is provided with various facilities such as a fuel storage facility 12, an LNG tank 14, a power generation facility 16, an LNG vaporizer 17, and the like. In the present embodiment, the two condensers 18A and 18B provided in the power generation facility 16 are cooled with seawater, and intake water for taking seawater from the sea 2 and supplying it to the condensers 18A and 18B, respectively. Roads 20A and 20B and a water discharge path 22 for releasing seawater that has passed through the condensers 18A and 18B to the sea 2 are installed. Seawater is taken in from the inlets 24A and 24B at the ends of the intake channels 20A and 20B, flows through the intake channels 20A and 20B, passes through the condensers 18A and 18B, respectively, and then passes through the discharge channel 22 common to both systems. It passes through the water outlet 26 at its tip and is discharged into the sea 2.

また、本実施形態では、放水路22を流れる海水の一部をLNG気化器17に循環させるためのLNG気化器流路27を放水路22から分岐させている。LNG気化器17は、LNG気化器流路27から供給される海水の熱によりLNGを気化させる。このように、冷却水として使用された後の海水でLNGを気化させることにより、復水器18で温められた海水を冷却してから海2へ放出することができるという効果も得られる。   In the present embodiment, the LNG vaporizer flow path 27 for circulating a part of the seawater flowing through the water discharge path 22 to the LNG vaporizer 17 is branched from the water discharge path 22. The LNG vaporizer 17 vaporizes LNG by the heat of seawater supplied from the LNG vaporizer flow path 27. Thus, by vaporizing LNG with seawater after being used as cooling water, the seawater warmed by the condenser 18 can be cooled and then released into the sea 2.

上記のように、取水路20、放水路22、及びLNG気化器流路27には海水が流れるため、流路内には貝等の海洋生物が付着・繁殖し易い。そして、流路内に多量の海洋生物が付着すると、流路が塞がれて十分な流量が得られなくなる等のために冷却性能が低下するおそれがある。特に、取水路20A,20Bについては、低い水温の海水を取り込めるように、取水口24A,24Bが陸地からかなり離れた沖合いに設けられるため、取水路20は非常に長くなって、海洋生物の付着の影響を受け易い。また、復水器18で温められた海水が流れるLNG気化器流路27内は海洋生物が繁殖し易い状態となっている。   As described above, since seawater flows through the intake channel 20, the discharge channel 22, and the LNG vaporizer channel 27, marine organisms such as shellfish are easily attached and propagated in the channel. If a large amount of marine organisms adhere to the flow path, the flow performance may be reduced because the flow path is blocked and a sufficient flow rate cannot be obtained. In particular, with regard to the intake channels 20A and 20B, the intake ports 24A and 24B are provided offshore so as to be able to take in seawater having a low water temperature. Susceptible to. The LNG vaporizer flow path 27 through which the seawater warmed by the condenser 18 flows is in a state where marine organisms are easy to breed.

そこで、本実施形態では、取水路20の取水口24の近傍位置及びLNG気化器流路27の入口近傍に、塩素系薬剤として次亜塩素酸ナトリウム溶液を注入することにより、取水路20、放水路22、及びLNG気化器流路27の内壁面において貝等の海洋生物の付着及び成長を抑制することとしている。ただし、次亜塩素酸ナトリウムに限らず、例えば二酸化塩素等の他の塩素系薬剤を用いてもよい。   Therefore, in the present embodiment, the sodium hypochlorite solution is injected as a chlorinated chemical into the vicinity of the intake port 24 of the intake channel 20 and the vicinity of the inlet of the LNG vaporizer channel 27, thereby allowing the intake channel 20 to be released. In the water channel 22 and the inner wall surface of the LNG vaporizer channel 27, adhesion and growth of marine organisms such as shellfish are suppressed. However, it is not limited to sodium hypochlorite, and other chlorinated chemicals such as chlorine dioxide may be used.

図2は、取水路20A,20B、放水路22、及びLNG気化器流路27からなる冷却水系統28を模式図的に示す。同図に示す如く、復水器18と取水路20A,20Bとの接続部には、夫々、海水ポンプ30A,30Bが設けられており、これら海水ポンプ30A、30Bにより海水が取水口24A,24Bから取水路20A,20Bへ吸入される。   FIG. 2 schematically shows a cooling water system 28 including intake channels 20 </ b> A and 20 </ b> B, a discharge channel 22, and an LNG vaporizer channel 27. As shown in the figure, seawater pumps 30A and 30B are provided at the connection portions between the condenser 18 and the intake channels 20A and 20B, respectively, and seawater is taken in by the seawater pumps 30A and 30B. To the intake channels 20A and 20B.

取水路20A,20Bの取水口24A,24Bの近傍には、夫々、薬剤注入部32A,32Bが設けられている。また、LNG気化器流路27の入口近傍には薬剤注入部32Cが設けられている。なお、薬剤注入部32A〜32Cは同様の構成を有しており、それらを総称する場合は薬剤注入部32という。   In the vicinity of the water intakes 24A and 24B of the water intake channels 20A and 20B, drug injection portions 32A and 32B are provided, respectively. Further, a drug injection part 32C is provided in the vicinity of the inlet of the LNG vaporizer flow path 27. The drug injection units 32A to 32C have the same configuration, and are collectively referred to as the drug injection unit 32.

放水路22の放水口26の近傍には、海2へ放出される海水中の残留塩素濃度を検出する残留塩素濃度計34が設けられている。残留塩素濃度計34による検出信号は無線又は有線で陸地上に設けられた監視装置へ送られる。   In the vicinity of the water outlet 26 of the water discharge channel 22, a residual chlorine concentration meter 34 for detecting the residual chlorine concentration in the seawater discharged to the sea 2 is provided. The detection signal from the residual chlorine concentration meter 34 is sent wirelessly or by wire to a monitoring device provided on land.

図3は、薬剤注入部32の詳細構成を示す。同図に示す如く、薬剤注入部32は、取水路20の内部に注入口41を有する注入管40、注入管40に次亜塩素酸ナトリウム溶液を供給する薬剤供給槽42、及び、注水路40に設けられたバルブ44により構成されており、バルブ44の開閉は、薬剤注入部32A〜32Cに共通の制御装置46により制御される。図3に示す例では、注入管40の先端が海水の下流側へ向けて屈曲され、その先端に注入口41が設けられている。なお、図4に示すように、注入管40の先端部の断面が注入口41へ向けて次第に拡がるように構成してもよい。また、図5に示すように、注入管40を屈曲させずに、その下流側側面に設けた穴を注入口41としてもよい。このように、注入口41として様々な構成が考えられる。   FIG. 3 shows a detailed configuration of the drug injection unit 32. As shown in the figure, the drug injection section 32 includes an injection pipe 40 having an injection port 41 inside the intake channel 20, a drug supply tank 42 for supplying a sodium hypochlorite solution to the injection pipe 40, and a water injection path 40. The opening / closing of the valve 44 is controlled by a control device 46 common to the drug injection parts 32A to 32C. In the example shown in FIG. 3, the tip of the injection tube 40 is bent toward the downstream side of the seawater, and an injection port 41 is provided at the tip. In addition, as shown in FIG. 4, you may comprise so that the cross section of the front-end | tip part of the injection tube 40 may spread toward the injection port 41 gradually. Further, as shown in FIG. 5, a hole provided on the downstream side surface may be used as the injection port 41 without bending the injection tube 40. Thus, various structures can be considered as the injection port 41.

なお、注入管40は、好ましくは、取水路20及びLNG気化器流路27の壁面近傍での残留塩素濃度が高くなるように、壁面に沿って取り付けられる。その場合、取水路20の底部には汚泥が堆積するため、側部又は上部に沿って取り付けるものとする。また、注入管40を複数本設けてもよい。   The injection pipe 40 is preferably attached along the wall surface so that the residual chlorine concentration in the vicinity of the wall surface of the intake channel 20 and the LNG vaporizer channel 27 is increased. In that case, since sludge accumulates in the bottom part of the intake channel 20, it shall be attached along a side part or an upper part. A plurality of injection tubes 40 may be provided.

図6(a)〜(c)は、夫々、制御装置46により制御される薬剤注入部32A〜32Cのバルブ44の開閉状態(すなわち、薬剤注入のオン/オフ状態)の時間変化を示す。同図に示すように、本実施形態では、冷却水系統28の3箇所に設けられた薬剤注入部32A,32B,32Cを順次切り替えて選択した何れかの薬剤注入部32から次亜塩素酸ナトリウム溶液を注入している。   FIGS. 6A to 6C show temporal changes in the open / closed state of the valve 44 of the drug injection sections 32A to 32C controlled by the control device 46 (that is, the on / off state of drug injection). As shown in the figure, in this embodiment, sodium hypochlorite is selected from any one of the drug injection parts 32 selected by sequentially switching the drug injection parts 32A, 32B, 32C provided at three locations of the cooling water system 28. The solution is being injected.

図7は、例えば、取水路20Aに設けられた薬剤注入部32Aから次亜塩素酸ナトリウム溶液を注入している状態での、冷却水系統28の各部の残留塩素濃度の分布を示す。同図に実線Iで示すように、薬剤注入部32Aから次亜塩素酸ナトリウム溶液が注入されることにより、取水路20Aの取水口24Aでの残留塩素濃度は高くなり、この濃度は下流側へ向かうにつれて次第に低下する。一方、取水路20Bについては次亜塩素酸ナトリウム溶液が注入されないため、同図に実線IIで示すように残留塩素濃度は全区間でゼロに近い値となっている。これら取水路20A,20Bを流れる海水は、復水器18A,18Bを通った後、一本の放水路22に合流する。このため、同図に実線IIIで示すように、放水路22Bの入口部分で海水中の塩素は薄められて、残留塩素濃度は取水路20Aの約半分に低下し、更に、放水口26へ向けて徐々に低下している。   FIG. 7 shows, for example, the distribution of residual chlorine concentration in each part of the cooling water system 28 in a state where a sodium hypochlorite solution is being injected from a drug injection part 32A provided in the intake channel 20A. As indicated by the solid line I in the figure, when the sodium hypochlorite solution is injected from the drug injection portion 32A, the residual chlorine concentration at the intake port 24A of the intake channel 20A is increased, and this concentration decreases downstream. It gradually decreases as you go. On the other hand, since the sodium hypochlorite solution is not injected into the intake channel 20B, the residual chlorine concentration is close to zero in the entire section as indicated by the solid line II in FIG. The seawater flowing through these intake channels 20A and 20B passes through the condensers 18A and 18B, and then merges into one discharge channel 22. For this reason, as shown by the solid line III in the figure, the chlorine in the seawater is diluted at the inlet portion of the discharge channel 22B, the residual chlorine concentration is reduced to about half of the intake channel 20A, and further toward the discharge port 26. It is gradually decreasing.

なお、図7に示す破線IVは、薬剤注入部32A,32Bの両方から連続的に次亜塩素酸ナトリウム溶液を注入しながら、放水口26から海2へ放出される海水の残留塩素濃度を上記実施形態と同程度に抑える場合の、取水路20A,20Bの残留塩素濃度分布を示している。この破線IVと上記実線Iとを対比して分かるように、本実施形態では、取水路20A,20Bにおける残留塩素濃度を、薬剤注入部32A,32Bの両方から連続的に次亜塩素酸ナトリウム溶液を注入する場合に比べて、2倍近い値に確保しながら(つまり、次亜塩素酸ナトリウム溶液の注入量又はその濃度として2倍近い値を用いながら)、海2へ放出される海水の残留塩素濃度を同程度に抑えることができる。   7 indicates the residual chlorine concentration of the seawater released from the outlet 26 to the sea 2 while continuously injecting the sodium hypochlorite solution from both the drug injection parts 32A and 32B. The residual chlorine concentration distribution of intake channel 20A, 20B in the case of restraining to the same extent as embodiment is shown. As can be seen by comparing the broken line IV with the solid line I, in this embodiment, the residual chlorine concentration in the intake channels 20A, 20B is continuously measured from both the chemical injection parts 32A, 32B. The amount of residual seawater released into the sea 2 while securing a value close to twice that when injecting water (that is, using a value almost twice as the injection amount or concentration of sodium hypochlorite solution) The chlorine concentration can be suppressed to the same level.

このように、本実施形態によれば、薬剤注入部32A〜32Cを順次切り替えて次亜塩素酸ナトリウム溶液を注入することにより、取水路20A,20Bでの残留塩素濃度を高くして、貝等の海洋生物の付着及び成長を効果的に抑制しつつ、海2へ放出される海水の残留塩素濃度を低く抑えることができるのである。   As described above, according to the present embodiment, by sequentially switching the drug injection parts 32A to 32C and injecting the sodium hypochlorite solution, the residual chlorine concentration in the intake channels 20A and 20B is increased, and shellfish and the like The residual chlorine concentration of the seawater released to the sea 2 can be kept low while effectively suppressing the adhesion and growth of marine organisms.

また、本実施形態では、暖められた海水が流れるために藻類及びバクテリア等の海洋生物が繁殖し易いLNG気化器流路27の入口部でも次亜塩素酸ナトリウム溶液を注入することにより、このLNG気化器流路27においても海洋生物の付着及び成長を効果的に抑制することができる。しかも、上記の通り、このLNG気化器流路27に設けられる薬剤注入部32Cを含めて、3つの薬剤注入部32A〜32Cを順次切り替えながら、何れかの薬剤注入部32から次亜塩素酸ナトリウム溶液を注入するようにしているので、LNG気化器流路27の残留塩素濃度も高くしつつ、海2へ放出される海水の残留塩素濃度を低く抑えることが可能となっている。   Further, in this embodiment, since the warmed seawater flows, the sodium chlorite solution is also injected into the inlet portion of the LNG vaporizer flow path 27 where marine organisms such as algae and bacteria are easy to breed. Also in the vaporizer channel 27, the adhesion and growth of marine organisms can be effectively suppressed. Moreover, as described above, the sodium hypochlorite is fed from any of the drug injection parts 32 while sequentially switching the three drug injection parts 32A to 32C including the drug injection part 32C provided in the LNG vaporizer flow path 27. Since the solution is injected, it is possible to keep the residual chlorine concentration of the seawater released to the sea 2 low while increasing the residual chlorine concentration of the LNG vaporizer flow path 27.

なお、上記実施形態では、LNG気化器流路27にも薬剤注入部32Cが設けられる構成としたが、LNG気化器流路27に薬剤注入部32が設けられない場合や、LNG気化器流路27自体が存在しない場合は、取水路20A,20Bの薬剤注入部32A,32Bを交互に切り替えて次亜塩素酸ナトリウム溶液を注入すればよい。また、取水路20の系統数は2系統に限らず、3系統以上設けられていてもよく、その場合には、各系統に薬剤注入部32を設けて、それらを順次切り替えて次亜塩素酸ナトリウム溶液を注入すればよい。また、取水路20が1系統のみ設けられる場合は、取水路20とLNG気化器流路27とに薬剤注入部32を設けて、それらを交互に切り替えて次亜塩素酸ナトリウム溶液を注入すればよい。要するに、冷却水系統を構成する少なくとも2つの流路に、夫々、塩素系薬剤を注入するための薬剤注入部を設け、それら薬剤注入部を順次切り替えて次亜塩素酸ナトリウム溶液等の塩素系薬剤を注入する構成であれば本発明の範囲に含まれる。   In the above embodiment, the LNG vaporizer flow path 27 is also provided with the drug injection part 32C. However, when the LNG vaporizer flow path 27 is not provided with the drug injection part 32, the LNG vaporizer flow path 27 is provided. When 27 itself does not exist, what is necessary is just to inject | pour a sodium hypochlorite solution by switching the chemical injection part 32A, 32B of intake channel 20A, 20B alternately. In addition, the number of intake channels 20 is not limited to two, and three or more systems may be provided. In that case, drug injection units 32 are provided in each system, and these are sequentially switched to hypochlorous acid. A sodium solution may be injected. In addition, when only one system of the intake channel 20 is provided, the drug injection unit 32 is provided in the intake channel 20 and the LNG vaporizer channel 27, and they are alternately switched to inject the sodium hypochlorite solution. Good. In short, at least two flow paths constituting the cooling water system are each provided with a drug injection part for injecting a chlorine-based drug, and the drug injection parts are sequentially switched to make a chlorine-based drug such as a sodium hypochlorite solution. If it is the structure which inject | pours, it is contained in the range of this invention.

また、上記実施形態では、火力発電所の復水器を冷却対象設備として冷却するものとしたが、本発明は復水器に限らず、海水を用いて各種設備を冷却する場合に広く適用が可能である。   In the above embodiment, the condenser of the thermal power plant is cooled as the equipment to be cooled. However, the present invention is not limited to the condenser and is widely applied when cooling various equipment using seawater. Is possible.

本発明の一実施形態に係わる火力発電所の概略平面図である。1 is a schematic plan view of a thermal power plant according to an embodiment of the present invention. 取水路、放水路、及びLNG気化器流路からなる冷却水系統を模式図的に示す。The cooling water system which consists of a water intake channel, a water discharge channel, and a LNG vaporizer flow path is shown typically. 薬剤注入部の詳細構成を示す図である。It is a figure which shows the detailed structure of a chemical | medical agent injection | pouring part. 注入管の注入口の構成例を示す図である。It is a figure which shows the structural example of the injection port of an injection tube. 注入管の注入口の別の構成例を示す図である。It is a figure which shows another structural example of the injection inlet of an injection tube. 図6(a)〜(c)は、夫々、3つの薬剤注入部32A〜32Cのバルブの開閉状態(すなわち、薬剤注入のオン/オフ状態)の時間変化を示す図である。FIGS. 6A to 6C are diagrams showing temporal changes in the open / closed states of the valves of the three drug injection units 32A to 32C (that is, the on / off states of drug injection), respectively. 取水路20Aに設けられた薬剤注入部32Aから次亜塩素酸ナトリウム溶液を注入している状態での、冷却水系統の各部の残留塩素濃度の分布を示す図である。It is a figure which shows distribution of the residual chlorine concentration of each part of a cooling water system | strain in the state which inject | pours the sodium hypochlorite solution from the chemical | medical agent injection | pouring part 32A provided in the intake channel 20A.

符号の説明Explanation of symbols

2 海
10 火力発電所
17 LNG気化器
18A,18B 復水器
20A,20B 取水路
22 放水路
24A,24B 取水口
26 放水口
27 LNG気化器流路
28 冷却水系統
30A,30B 海水ポンプ
32(32A,32B,32C) 薬剤注入部
40 注入管
41 注入口
42 薬剤供給槽
44 バルブ
46 制御装置
2 Sea 10 Thermal power plant 17 LNG vaporizer 18A, 18B Condenser 20A, 20B Intake channel 22 Discharge channel 24A, 24B Intake port 26 Discharge port 27 LNG vaporizer channel 28 Cooling water system 30A, 30B Seawater pump 32 (32A , 32B, 32C) Drug injection part 40 Injection pipe 41 Inlet 42 Drug supply tank 44 Valve 46 Control device

Claims (5)

冷却水として海から海水を取り入れて冷却対象設備に供給し、この冷却対象設備を通った後の海水を海へ放出するための冷却水系統内において海洋生物の付着及び成長を抑制する方法であって、
前記冷却水系統を構成する複数の流路のうち少なくとも2つの流路に、夫々、塩素系薬剤を注入するための薬剤注入部を設け、それら薬剤注入部の中から順次切り替えて選択した薬剤注入部により該当する流路内へ塩素系薬剤を注入することを特徴とする方法。
This is a method for suppressing the adhesion and growth of marine organisms in the cooling water system for taking seawater from the sea as the cooling water and supplying it to the equipment to be cooled and discharging the seawater that has passed through this equipment to the sea. And
A drug injection unit for injecting a chlorine-based drug is provided in at least two of the plurality of channels constituting the cooling water system, and the drug injection selected by sequentially switching from among the drug injection units A method comprising injecting a chlorinated drug into a corresponding flow path by a section.
前記塩素系薬剤として次亜塩素酸ナトリウムを注入することを特徴とする請求項1記載の方法。   The method according to claim 1, wherein sodium hypochlorite is injected as the chlorinated drug. 前記冷却水系統は、海から取り込んだ海水を複数の前記冷却対象設備へ夫々送るための複数の取水路と、前記冷却対象設備を通過した海水を海へ放出するための放水路とを含んでおり、
前記薬剤注入部を前記複数の取水路の夫々の取水口近傍に設けることを特徴とする請求項1又は2記載の方法。
The cooling water system includes a plurality of intake channels for sending seawater taken from the sea to the plurality of facilities to be cooled, and a water discharge channel for releasing seawater that has passed through the facilities to be cooled to the sea. And
The method according to claim 1 or 2, wherein the medicine injection part is provided in the vicinity of each water intake port of the plurality of water intake channels.
前記冷却対象設備は、液化天然ガス(LNG)火力発電所に設けられた設備であり、前記放水路を流れる海水をLNG気化器に循環させるためのLNG気化器流路が設けられており、
少なくとも一つの前記薬剤注入部を前記LNG気化器流路に設けることを特徴とする請求項1〜3のうち何れか1項記載の方法。
The facility to be cooled is a facility provided in a liquefied natural gas (LNG) thermal power plant, and is provided with an LNG vaporizer flow path for circulating seawater flowing through the water discharge channel to the LNG vaporizer,
The method according to any one of claims 1 to 3, wherein at least one drug injection part is provided in the LNG vaporizer flow path.
冷却水として海から海水を取り入れて冷却対象設備に供給し、この冷却対象設備を通った後の海水を海へ放出するための冷却水系統内において海洋生物の付着及び成長を抑制するシステムであって、
前記冷却水系統を構成する複数の流路のうち少なくとも2つの流路に設けられた、塩素系薬剤を注入するための薬剤注入部と、
前記複数の薬剤注入部の中から順次切り替えて選択した薬剤注入部により該当する流路内へ塩素系薬剤を注入させる制御手段と、を備えることを特徴とするシステム。

It is a system that suppresses the adhesion and growth of marine organisms in the cooling water system for taking seawater from the sea as the cooling water and supplying it to the equipment to be cooled, and releasing the seawater that has passed through this equipment to the sea. And
A drug injection part for injecting a chlorine-based drug, provided in at least two channels among the plurality of channels constituting the cooling water system;
A control means for injecting a chlorinated drug into a corresponding flow path by a drug injection unit selected by switching sequentially from the plurality of drug injection units.

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