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JP4500071B2 - Dialysis equipment cleaning, disinfection wastewater neutralization treatment equipment - Google Patents

Dialysis equipment cleaning, disinfection wastewater neutralization treatment equipment Download PDF

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JP4500071B2
JP4500071B2 JP2004066339A JP2004066339A JP4500071B2 JP 4500071 B2 JP4500071 B2 JP 4500071B2 JP 2004066339 A JP2004066339 A JP 2004066339A JP 2004066339 A JP2004066339 A JP 2004066339A JP 4500071 B2 JP4500071 B2 JP 4500071B2
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waste liquid
alkaline
acidic
storage tank
dialysis
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節夫 小林
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    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
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    • Y02W10/37Wastewater or sewage treatment systems using renewable energies using solar energy

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本発明は透析排水のなかで、酸性或いはアルカリ性に傾いている洗浄,消毒廃液を中和処理する透析機器の洗浄,消毒廃液の中和処理装置に関する。  TECHNICAL FIELD The present invention relates to cleaning that is inclined toward acidity or alkalinity in dialysis wastewater, cleaning of dialysis equipment that neutralizes disinfecting waste liquid, and neutralizing treatment apparatus for disinfecting waste liquid.

人工透析を行う病院,診療所等では透析終了後に、例えば水洗−酸洗浄−水洗−薬洗−水洗といった工程を経る透析機器の消毒,洗浄がなされる。酸洗浄には酢酸などの酸性洗浄水が、薬洗には次亜塩素酸ナトリウムなどのアルカリ洗浄水が用いられる。これに伴ってアルカリ性(酸性)に傾いた廃液や酸性(アルカリ性)に傾いた廃液が排出される。両廃液は水質基準内に収まっていないため、それぞれ中和処理してから下水道へ流されることとなる。斯る透析機器の洗浄,消毒廃液を中和処理する装置はこれまでいくつか提案されてきた(例えば、特許文献1,2参照)。  In hospitals, clinics, and the like where artificial dialysis is performed, after dialysis is completed, dialysis equipment is sterilized and cleaned through processes such as water washing, acid washing, water washing, drug washing, and water washing. Acid cleaning water such as acetic acid is used for the acid cleaning, and alkaline cleaning water such as sodium hypochlorite is used for the chemical cleaning. Along with this, waste liquid inclined to alkaline (acidic) and waste liquid inclined to acidic (alkaline) are discharged. Since both waste liquids do not fall within the water quality standards, they will be neutralized before being discharged into the sewer. Several apparatuses for neutralizing the dialysis machine washing and disinfecting waste liquid have been proposed so far (see, for example, Patent Documents 1 and 2).

特開2001−269670公報(第1−4頁)          JP 2001-269670 A (page 1-4) 特開平5−38495号公報(第1−3頁)          Japanese Patent Laid-Open No. 5-38495 (page 1-3)

しかるに、特開2001−269670公報技術(従来技術1)は、酸中和槽に炭酸カルシウムを主成分とする天然岩石粒子を充填しているため中和反応が遅く、天然岩石粒子を大量に充填しなければならなかった。そして天然岩石粒子を用いていることから中和処理が進むと黒いアクが現れてきたりするのでそれを除去しなければならなかった。また、次亜塩素酸ナトリウム水溶液のアルカリ性廃液については、水道水を加えるだけで特に処理がなされていなかった。
これに対し、特開平5−38495号公報技術(従来技術2)は、前記次亜塩素酸ナトリウム等の塩素系酸化剤を含む病院排水に還元剤を添加する発明が提案されている。しかし、従来技術2は次亜塩素酸ナトリウム含有廃液を浄化処理するのに、別途、亜硫酸ナトリウム溶液等の還元剤を要していた。
また、これまでの透析機器の洗浄,消毒廃液の中和処理装置はアルカリ性廃液を受け入れる貯液槽と酸性廃液を受け入れる貯液槽が同じであったために時として問題が生じた。次亜塩素酸ナトリウム等のアルカリ性廃液は酸性で有毒の塩素ガスを発生するため、酸性廃液が入った貯液槽に次亜塩素酸ナトリウム等のアルカリ性廃液が導入されたり、逆に次亜塩素酸ナトリウム等のアルカリ性廃液が入った貯液槽に酸性廃液が流れ込んできたりすると危険な場合があった。
However, Japanese Patent Laid-Open No. 2001-269670 (Prior Art 1) is filled with natural rock particles mainly composed of calcium carbonate in an acid neutralization tank, so the neutralization reaction is slow, and a large amount of natural rock particles are filled. Had to do. And since natural rock particles were used, black acupuncture appeared when neutralization proceeded, so it had to be removed. Moreover, about the alkaline waste liquid of sodium hypochlorite aqueous solution, only the tap water was added and the process was not made especially.
In contrast, Japanese Patent Laid-Open No. 5-38495 (prior art 2) proposes an invention in which a reducing agent is added to hospital wastewater containing a chlorine-based oxidizing agent such as sodium hypochlorite. However, Conventional Technique 2 requires a reducing agent such as a sodium sulfite solution separately to purify the sodium hypochlorite-containing waste liquid.
In addition, the conventional dialysis machine cleaning and disinfecting waste liquid neutralization treatment apparatus sometimes has problems because the storage tank for receiving the alkaline waste liquid and the storage tank for receiving the acidic waste liquid are the same. Since alkaline waste liquid such as sodium hypochlorite generates acidic and toxic chlorine gas, alkaline waste liquid such as sodium hypochlorite is introduced into the storage tank containing the acidic waste liquid, or conversely hypochlorous acid. In some cases, the acidic waste liquid may flow into the storage tank containing the alkaline waste liquid such as sodium.

本発明は上記問題点を解決するもので、透析排水のなかで酸性或いはアルカリ性に傾いている洗浄,消毒廃液を、個別に且つ安全に中和処理し、しかも低コストで処理することのできる透析機器の洗浄,消毒廃液の中和処理装置を提供することを目的とする。  The present invention solves the above-mentioned problems. Dialysis wastewater that is inclined toward acidity or alkalinity in dialysis wastewater can be individually and safely neutralized and treated at low cost. An object is to provide a neutralization treatment device for cleaning equipment and disinfecting waste liquid.

上記目的を達成すべく、請求項1に記載の発明の要旨は、透析終了後の消毒,洗浄で発生する酸性廃液を受け入れる酸性廃液専用の酸性貯液槽と、水に溶解してアルカリ性を呈する粒状物が槽内に充填された酸中和槽と、を具備し、前記酸性貯液槽に溜めた酸性廃液を前記酸中和槽に送液し中和処理をなすと共に、透析終了後の消毒,洗浄で発生するアルカリ性廃液を受け入れるアルカリ性廃液専用のアルカリ性貯液槽をさらに具備し、アルカリ性廃液を中和処理するようにし、且つ、透析終了後の消毒,洗浄で発生する廃液を、前記酸性貯液槽へ移送する配管と前記アルカリ性貯液槽へ移送する配管と一般下水道へ移送する一般放流配管とに分岐してなる3系統の配管と、これら3系統の配管それぞれに前記廃液を送液できるよう切替え可能な切替バルブと、該切替バルブを開閉制御する制御盤と、を具備することを特徴とする透析機器の洗浄,消毒廃液の中和処理装置にある。
請求項2に記載の発明たる透析機器の洗浄,消毒廃液の中和処理装置は、請求項1で、アルカリ性貯液槽内にエアバブリング発生器を具備し、次亜塩素酸ナトリウム含有廃液からなるアルカリ性廃液をエアバブリングさせて中和処理するようにしたことを特徴とする。
In order to achieve the above-mentioned object, the gist of the invention described in claim 1 is that an acidic storage tank dedicated to an acidic waste liquid that accepts an acidic waste liquid generated by disinfection and washing after dialysis is completed, and is alkaline when dissolved in water. granules anda acid neutralization tank filled in the bath, an acidic waste liquid accumulated in said acidic liquid reservoir with liquid feed neutralizing process to be in the acid neutralization tank, after completion of the dialysis In addition, an alkaline storage tank dedicated to alkaline waste liquid that receives the alkaline waste liquid generated by disinfection and washing of the liquid is further provided to neutralize the alkaline waste liquid , and the waste liquid generated by disinfection and washing after the completion of dialysis Three lines of piping branching into a pipe for transferring to the acidic storage tank, a pipe for transferring to the alkaline storage tank, and a general discharge pipe for transferring to the general sewer, and the waste liquid is sent to each of these three lines. Switchable to allow liquid And replacement valve, cleaning of the dialysis apparatus, characterized by comprising a control panel to open and close control of the said switching valve is in the neutralization apparatus disinfecting waste.
The neutralization treatment apparatus for washing and disinfecting waste liquid for dialysis equipment according to claim 2 is the neutralizing apparatus for waste liquid according to claim 1, comprising an air bubbling generator in an alkaline liquid storage tank, and comprising a sodium hypochlorite-containing waste liquid. It is characterized in that the alkaline waste liquid is neutralized by air bubbling.

(作用)
請求項1の発明のごとく、透析終了後の消毒,洗浄で発生する酸性廃液を受け入れる酸性廃液専用の酸性貯液槽と、水に溶解してアルカリを呈する粒状物が槽内に充填された酸中和槽と、を具備し、前記酸性貯液槽に溜めた酸性廃液を前記酸中和槽に送液し中和処理をなすと、透析終了後の消毒,洗浄で発生する廃液のうち酸性廃液だけを個別に処理するのでその量も少なくなって効率良く処理できる。また、酸性廃液専用の酸性貯液槽と、水に溶解してアルカリを呈する粒状物が槽内に充填された酸中和槽とに分けると、一日のうちで限られた時間帯しか排出されない酸性廃液を一旦酸性貯液槽に溜め、次の酸性廃液が排出される時までに酸中和槽へ徐々に流してその時間帯を使って有効且つ確実に処理できる。また斯る構成をとることによって、酸性廃液を処理する中和装置をコンパクト化できる。
析終了後の消毒,洗浄で発生するアルカリ性廃液を受け入れるアルカリ性廃液専用のアルカリ性貯液槽をさらに具備し、アルカリ性廃液を中和処理するようにすると、透析終了後の消毒,洗浄で発生する廃液のうち酸性廃液のみならずアルカリ性廃液も個別処理でき、酸性廃液が入った貯液槽に次亜塩素酸ナトリウム等のアルカリ性廃液が導入されるといったトラブルが解消する。そして、次亜塩素酸ナトリウム等のアルカリ性廃液を無害化処理できるので、微生物を死滅させたり放流下水道に負担をかけずに済む。
透析終了後の消毒,洗浄で発生する廃液を、酸性貯液槽へ移送する配管とアルカリ性貯液槽へ移送する配管と一般下水道へ移送する一般放流配管とに分岐してなる3系統の配管と、これら3系統の配管それぞれに前記廃液を送液できるよう切替え可能な切替バルブと、該切替バルブを開閉制御する制御盤とを備えると、透析終了後の消毒,洗浄で発生する廃液のうち、酸性廃液は酸性廃液の中和処理装置に導き、またアルカリ性廃液はアルカリ性廃液の中和処理装置に導き、また中和処理のいらない水洗廃液はそのまま一般放流して下水道施設に委ねることが可能になり、中和処理が必要なその廃液だけを選択的に処理でき、無駄を省き効率的且つ経済的な中和装置となる。
請求項2の発明のごとく、アルカリ性貯液槽内にエアバブリング発生器を具備し、次亜塩素酸ナトリウム含有廃液からなるアルカリ性廃液をエアバブリングさせて中和処理するようにすると、薬剤を用いずに中和処理が可能になり、運転コストが殆どかからずまた環境に優しい装置となる。
(Function)
As in the first aspect of the present invention, an acid storage tank dedicated to the acidic waste liquid that receives the acidic waste liquid generated by disinfection and washing after dialysis is completed, and an acid filled with granular materials that dissolve in water and exhibit alkali. A neutralization tank, and when the acid waste liquid stored in the acid storage tank is fed to the acid neutralization tank and neutralized, it is acidic among the waste liquid generated by disinfection and washing after dialysis. Since only the waste liquid is processed individually, the amount of the waste liquid is reduced and the waste liquid can be processed efficiently. In addition, when the acid storage tank dedicated to acidic waste liquid and the acid neutralization tank that is dissolved in water and presents alkali are filled in the tank, it is discharged only within a limited time of the day. The acidic waste liquid that is not used can be once stored in the acidic liquid storage tank, and gradually flowed to the acid neutralization tank until the next acidic waste liquid is discharged, so that it can be effectively and reliably treated using the time zone. Moreover, the neutralization apparatus which processes an acidic waste liquid can be compactized by taking such a structure.
Dialysis after completion of disinfection, the alkaline waste solution only alkaline reservoir of accepting the alkaline waste liquid generated by washing further comprising, when so as to neutralize the alkaline liquid waste, waste liquid generated disinfected after completion of the dialysis, in washing Among them, not only acidic waste liquid but also alkaline waste liquid can be individually treated, and troubles such as introduction of alkaline waste liquid such as sodium hypochlorite into the storage tank containing the acidic waste liquid are solved. And since alkaline waste liquids, such as sodium hypochlorite, can be detoxified, it is not necessary to kill microorganisms or put a burden on the discharged sewer.
Three systems of pipes that branch into a pipe for transferring waste liquid generated by disinfection and washing after dialysis to an acidic storage tank, a pipe for transferring to an alkaline storage tank, and a general discharge pipe for transferring to a general sewer. In addition, a switching valve that can be switched so that the waste liquid can be fed to each of these three pipes, and a control panel that controls the opening and closing of the switching valve, the waste liquid generated by disinfection and washing after the completion of dialysis, It is possible to lead acidic waste liquid to the neutralization treatment equipment for acidic waste liquid, alkaline waste liquid to the neutralization treatment equipment for alkaline waste liquid, and discharge waste water that does not require neutralization treatment to the sewerage facility as it is. Thus, only the waste liquid that needs neutralization can be selectively treated, and an efficient and economical neutralization apparatus can be obtained without waste.
As in the second aspect of the present invention, when an alkaline liquid storage tank is equipped with an air bubbling generator and the alkaline waste liquid composed of sodium hypochlorite-containing waste liquid is neutralized by air bubbling, no chemical is used. In addition, the neutralization treatment can be performed, and the operation cost is hardly required and the apparatus is environmentally friendly.

本発明の透析機器の洗浄,消毒廃液の中和処理装置は、透析排水のなかで酸性或いはアルカリ性に傾いている洗浄,消毒廃液を、個別に効率良くしかも安全に中和処理ができ、加えて、装置がコンパクト化しまた運転コストも安くなるなど優れた効果を発揮する。  The neutralization treatment apparatus for cleaning and disinfecting waste liquid of the dialysis machine of the present invention can neutralize the cleaning and disinfecting waste liquid that is inclined to acidity or alkalinity in dialysis waste water individually and efficiently. The device is more compact and the operation cost is reduced.

以下、本発明に係る透析機器の洗浄,消毒廃液の中和処理装置の一形態を詳述する。図1は透析機器の洗浄,消毒廃液の中和処理装置の概略平面図、図2はアルカリ性廃液の中和処理装置に係る一部縦断面説明図、図3は図2のエアバブリング供給具の説明斜視図、図4は酸性廃液の中和処理装置に係る一部縦断面説明図である。  Hereinafter, an embodiment of a neutralization treatment apparatus for washing and disinfecting waste liquid for dialysis equipment according to the present invention will be described in detail. FIG. 1 is a schematic plan view of a neutralization treatment apparatus for cleaning and disinfecting waste liquid of dialysis equipment, FIG. 2 is a partial longitudinal cross-sectional explanatory view of the neutralization treatment apparatus for alkaline waste liquid, and FIG. FIG. 4 is an explanatory perspective view, and FIG. 4 is a partial vertical cross-sectional explanatory view of an acidic waste liquid neutralizing apparatus.

本実施形態の透析機器の洗浄,消毒廃液の中和処理装置(以下、単に「中和処理装置」という。)は、酸性廃液XLの中和処理装置1(以下、「酸性中和装置」という。)とアルカリ性廃液YLの中和処理装置(以下、「アルカリ性中和装置」という。)とを備える。ここでは、酸性中和装置Aの構成要素たる酸性貯液槽1と酸中和槽2と処理水受け具3とを一体化し、さらに補強立板部fと補強底板部fを付加して箱形容器Aにする。またアルカリ性中和装置Bの構成要素たるアルカリ性貯液槽6と処理水受け具3とを一体化し、さらに補強立板部fと補強底板部fを付加して箱形容器Bにする。加えて、箱形容器Aと箱形容器Bの接合部を共用して一つのボックス型の箱形容器に一体化して中和処理装置をコンパクト化する。箱形容器A,Bには図示しない上蓋が適宜被せられる。The neutralization treatment apparatus (hereinafter simply referred to as “neutralization treatment apparatus”) for cleaning and disinfecting waste liquid of the dialysis apparatus of the present embodiment is referred to as neutralization treatment apparatus 1 for acidic waste liquid XL (hereinafter referred to as “acid neutralization apparatus”). And a neutralization treatment device for alkaline waste liquid YL (hereinafter referred to as “alkaline neutralization device”). Here, by integrating the components serving acidic reservoir 1 and an acid neutralization tank 2 and treated water receptacle 3 acidic neutralizer A, and further added with reinforcing standing portion f 2 the reinforcement bottom plate portion f 1 to box-shaped container A 1 Te. Also, the alkaline liquid storage tank 6 and the treated water receptacle 3 which are constituent elements of the alkaline neutralizer B are integrated, and a reinforcing upright plate portion f 2 and a reinforcing bottom plate portion f 1 are added to form a box-shaped container B 1 . . In addition, compact neutralization treatment apparatus is integrated into a box-shaped container of one box-type share a junction box-shaped container A 1 and the box-shaped container B 1. The box-shaped containers A 1 and B 1 are appropriately covered with an upper lid (not shown).

(1)酸性中和装置
酸性中和装置Aは、酸性貯液槽1と酸中和槽2と処理水受け具3と、水に溶解してアルカリを呈する粒状物(以下、「中和剤」という。)と、水供給具5とを具備する(図1,図4)。
(1) Acid Neutralizer An acid neutralizer A is an acid storage tank 1, an acid neutralizer 2, a treated water receptacle 3, and a granular material that dissolves in water and exhibits alkali (hereinafter referred to as "neutralizer"). And a water supply 5 (FIGS. 1 and 4).

酸性貯液槽1は立板部10と底板部11とを備えて上面開口の受槽を形成した酸性廃液専用槽で、透析終了後の消毒,洗浄で発生する例えば一日分の酸性廃液XLを受け入れるに十分な容量を有する。ここでは、箱形容器Aを区画化形成した酸性貯液槽1とし、隣接配置される酸中和槽2側の共用立板部10(20)の高さを他部分より一段低く設定する。図4に示すように酸性廃液XLの液面XLが前記立板部10のレベルを超えたときにオーバーフローして、酸性貯液槽1から酸中和槽2へ酸性廃液XLが流れ出すようにするためである。酸性貯液槽1の底板部11には、透析終了後の消毒,洗浄で発生する廃液のうち、酸性廃液XLを酸性貯液槽1に導く酸性廃液分岐管XPの開口XPが設けられる(図1)。酸性廃液分岐管XPの開口先端部が底板部11から若干上方に向け突出する。The acidic storage tank 1 is a tank for exclusive use of an acidic waste liquid having a standing plate portion 10 and a bottom plate portion 11 and forming a receiving tank having an upper surface opening. For example, the acidic waste liquid XL for one day generated by disinfection and washing after dialysis is obtained. Has enough capacity to accept. Here, the box-shaped container A 1 is defined as an acid storage tank 1 formed into compartments, and the height of the shared upright plate portion 10 (20) on the side of the acid neutralization tank 2 disposed adjacently is set to be one step lower than the other portions. . As shown in FIG. 4, when the liquid level XL 1 of the acidic waste liquid XL exceeds the level of the vertical plate portion 10, the acidic waste liquid XL flows out from the acidic storage tank 1 to the acid neutralization tank 2. It is to do. The bottom plate portion 11 of the acidic liquid storage tank 1 is provided with an opening XP 0 of the acidic waste liquid branch pipe XP that guides the acidic waste liquid XL to the acidic liquid storage tank 1 out of the waste liquid generated by disinfection and washing after dialysis. FIG. 1). The opening tip of the acidic waste liquid branch pipe XP protrudes slightly upward from the bottom plate 11.

酸中和槽2は立板部20と底板部21と仕切板23と隔板24と上下網状体25,26とを備える容器である。ここでの酸中和槽2は、箱形容器Aを区画化形成して立板部20と底板部21でつくられる上面開口容器である。酸中和槽2は図4のごとく該上面開口容器を仕切板23で左右二分割し、さらにこの分割された槽内を2枚の隔板24で分けている。隔板24の下縁と底板部21とは必要長さ分だけ離れ、また図4に示すように左方の立板部20から右方に隔板24,仕切板23,隔板24,右方立板部20へとそれらの上縁が右下がりになるよう段差が設けられる。槽全体が4室に分けられた格好の酸中和槽2では、酸性貯液槽1の例えば酸性廃液XLが一杯になり溢れるようになると、図4で、左方の立板部20(10)の上縁を乗り越え、酸性貯液槽1からオーバーフローで第1室に入り込んだ酸性廃液XLがまずダウンフローし、次に隔板24を潜って第2室をアップフローで上昇する。続いて、酸性廃液XLが仕切板23の堰を乗り越え、第3室に入ってダウンフローした後、隔板24を潜って第4室を上昇し、この第4室を上昇した廃水は下流側の立板部20の堰を乗り越えて処理水受け具3へと流れ出る。両隔板24の下縁近くには各室の流路を横切る下網状体25が水平配設され、さらに該網状体25上に中和剤4が充填される構成とする。かくして、酸中和槽2は中和剤4が所定量充填されることによって酸性貯液槽1から送り込まれる酸性廃液XLを中和処理する処理槽になっている。ここでは下網状体25上に充填された中和剤4の上にも上網状体26を被せ、中和剤4が不用意に流出しないようにしている。
網状体25は酸中和槽2内に充填される中和剤4を保持し、液体は通過させることのできるもので、ここでいう網状体はネットの他、多孔板や簀等を含む概念で用いる。本実施形態では網状体25にネットを使用し、該ネットは立板部20や仕切板23或いは隔板24によって形成された4つの筒部(4室)内で、底板部21から上方位置の隔板24の下縁近くに水平に張られている。
The acid neutralization tank 2 is a container provided with a standing plate portion 20, a bottom plate portion 21, a partition plate 23, a partition plate 24, and upper and lower mesh bodies 25 and 26. Here acid neutralization tank 2 in a top opening containers made with standing portion 20 and the bottom plate portion 21 to partition forming a box-shaped container A 1. As shown in FIG. 4, the acid-neutralizing tank 2 divides the upper surface opening container into two parts on the left and right with a partition plate 23, and further divides the inside of the divided tank into two partition plates 24. The lower edge of the partition plate 24 and the bottom plate portion 21 are separated by a necessary length, and as shown in FIG. 4, the partition plate 24, the partition plate 23, the partition plate 24, the right side from the left standing plate portion 20 to the right. A step is provided to the vertical plate portion 20 so that the upper edge thereof is lowered to the right. In the preferred acid neutralization tank 2 in which the entire tank is divided into four chambers, for example, when the acidic waste liquid XL in the acidic liquid storage tank 1 becomes full and overflows, the left vertical plate 20 (10 The acidic waste liquid XL that has climbed over the upper edge and entered the first chamber due to overflow from the acidic storage tank 1 first flows down, then goes down the partition plate 24 and ascends in the second chamber. Subsequently, the acidic waste liquid XL gets over the weir of the partition plate 23, enters the third chamber and flows down, and then goes down the partition plate 24 and ascends the fourth chamber. It flows over the weir of the standing plate portion 20 and flows out to the treated water receiver 3. In the vicinity of the lower edges of both the partition plates 24, a lower mesh member 25 is disposed horizontally across the flow path of each chamber, and the neutralizer 4 is filled on the mesh member 25. Thus, the acid neutralization tank 2 is a treatment tank that neutralizes the acidic waste liquid XL fed from the acidic storage tank 1 by being charged with a predetermined amount of the neutralizing agent 4. Here, the upper mesh body 26 is also put on the neutralizing agent 4 filled on the lower mesh body 25 so that the neutralizing agent 4 does not flow out carelessly.
The net-like body 25 holds the neutralizing agent 4 filled in the acid neutralization tank 2 and allows liquid to pass through. The net-like body here is a concept including a perforated plate, a flaw and the like in addition to the net. Used in. In this embodiment, a net is used for the net-like body 25, and the net is located above the bottom plate portion 21 in the four cylindrical portions (four chambers) formed by the standing plate portion 20, the partition plate 23, or the partition plate 24. It is stretched horizontally near the lower edge of the partition plate 24.

処理水受け具3は、酸性廃液XLが前記酸中和槽2で処理された処理水を受け取り、その処理水を酸性廃液の処理水配管XSPへと導く仲介受け具である。本処理水受け具3はコーン状漏斗とし、酸中和槽2の下流側(図4では酸中和槽2の右側)に隣接配置される。処理水受け具3の上縁を酸中和槽2に係る下流側の立板部20の外壁に当接させると共に、箱形容器Aを形成する補強立板部fの内壁に当接させて、酸中和槽2から流れ出る処理水を確実に捕捉する。処理水受け具3の下部は酸性廃液の処理水配管XSPにつながり、酸性廃液分岐管XPから取り込まれた酸性廃液XLが酸性貯液槽1,酸中和槽2,処理水受け具3を経由してこの処理水配管XSPに送られるようになっている。The treated water receptacle 3 is an intermediary receptacle that receives the treated water treated with the acid waste liquid XL in the acid neutralization tank 2 and guides the treated water to the treated water piping XSP of the acidic waste liquid. The treated water receptacle 3 is a cone funnel, and is disposed adjacent to the downstream side of the acid neutralization tank 2 (on the right side of the acid neutralization tank 2 in FIG. 4). It is brought into contact to the outer wall of the downstream side of the upright plate portion 20 of the upper edge of the treated water receptacle 3 into acid neutralization tank 2, abutting the inner wall of the reinforcement vertical plate portions f 2 to form a box-shaped container A 1 The treated water flowing out from the acid neutralization tank 2 is surely captured. The lower part of the treated water receptacle 3 is connected to the treated waste water pipe XSP of the acidic waste liquid, and the acidic waste liquid XL taken from the acidic waste liquid branch pipe XP passes through the acidic storage tank 1, the acid neutralization tank 2, and the treated water receptacle 3. Then, it is sent to the treated water pipe XSP.

中和剤4は水に溶解してアルカリを呈する粒状物である。本実施形態は、水酸化マグネシウム又は酸化マグネシウムを主成分とする粒状物を用い、より詳しくは海水法水酸化マグネシウムによって得られる粒径が3mm〜5mmの水酸化マグネシウム粒状物又はそれを所定温度で焼成した酸化マグネシウムを用いている。具体的には宇部マテリアルズ株式会社製の水酸化マグネシウム粒状物4aを用いる。海水法水酸化マグネシウムは、「脱炭酸海水に消石灰乳を添加して生成されるが、その水酸化マグネシウムではコロイド状となり沈降及び洗浄が困難になるので、種晶循環を実施し、粒子を大きくして沈降性,濾過性の良い水酸化マグネシウムが得られる」(『13398の化学商品』,化学工業日報社,165頁,1998)ことから、これを酸性中和装置Aで用いても酸中和処理中にアク等が出ず、またその粒径も適度な大きさで、取扱いに優れたものとなっている。  The neutralizing agent 4 is a granular material that dissolves in water and exhibits an alkali. In the present embodiment, a granular material containing magnesium hydroxide or magnesium oxide as a main component is used, and more specifically, a magnesium hydroxide granular material having a particle diameter of 3 mm to 5 mm obtained by seawater method magnesium hydroxide or a predetermined temperature. Calcinated magnesium oxide is used. Specifically, magnesium hydroxide granular material 4a manufactured by Ube Materials Co., Ltd. is used. Seawater magnesium hydroxide is produced by adding slaked lime milk to decarbonated seawater, but the magnesium hydroxide becomes colloidal and difficult to settle and wash. Thus, magnesium hydroxide with good sedimentation and filterability can be obtained ”(“ Chemical Products of 13398 ”, Chemical Industry Daily, page 165, 1998). No ak or the like is produced during the sum treatment, and the particle size thereof is moderate and excellent in handling.

水供給具5は酸性貯液槽1に水を送り込む器具である。ここでは水道管につなげる接続配管51と、水の制御用コンピュータ52と酸性貯液槽1内に水道水を導入する導入管53とを備える。
水の制御用コンピュータとして本実施形態は園芸用の潅水コンピュータ52を使用する。潅水コンピュータ52を用いて適切な時刻を選定して間欠運転を行うことができる。導入管53はその先端部が酸性貯液槽1内の酸中和槽2寄りに配され、底板部21近くで先端ノズル531が酸性廃液分岐管XPの導入側にそのノズル口を向けて設置される(図1,図4)。潅水コンピュータ52で制御された水道水が間欠的に先端ノズル531から噴出する。該水道水の水圧を利用して酸性貯液槽1内に溜まった酸性廃液XLを循環させて、順次、該酸性廃液XLを酸性貯液槽1から立板部10を乗り越え、オーバフロー(溢流)させて酸中和槽2へと流出させることができる。
The water supply tool 5 is an instrument for feeding water into the acidic storage tank 1. Here, a connection pipe 51 connected to the water pipe, a water control computer 52 and an introduction pipe 53 for introducing the tap water into the acidic liquid storage tank 1 are provided.
In this embodiment, a watering computer 52 for horticulture is used as the water control computer. An appropriate time can be selected using the irrigation computer 52 and intermittent operation can be performed. The leading end of the introduction pipe 53 is arranged near the acid neutralization tank 2 in the acidic liquid storage tank 1, and the tip nozzle 531 is installed near the bottom plate 21 with the nozzle opening facing the introduction side of the acidic waste liquid branch pipe XP. (FIGS. 1 and 4). Tap water controlled by the irrigation computer 52 is intermittently ejected from the tip nozzle 531. The acidic waste liquid XL accumulated in the acidic liquid storage tank 1 is circulated using the water pressure of the tap water, and the acidic waste liquid XL is sequentially passed over the vertical plate portion 10 from the acidic liquid storage tank 1 to overflow (overflow) ) To be discharged to the acid neutralization tank 2.

(2)アルカリ性中和装置
次に、アルカリ性中和装置Bについて詳述する。アルカリ性中和装置Bはアルカリ性貯液槽6と処理水受け具7とエアバブリング供給具8と水供給具9とを具備する。
(2) Alkaline neutralizer Next, the alkaline neutralizer B will be described in detail. The alkaline neutralizer B includes an alkaline liquid storage tank 6, a treated water receiver 7, an air bubbling supply tool 8, and a water supply tool 9.

アルカリ性貯液槽6は立板部60と底板部61とを備えて上面開口のボックス型受槽を形成したアルカリ性廃液専用槽で、透析終了後の消毒,洗浄で発生する例えば一日分のアルカリ性廃液YLを受け入れるに十分な容量を有する。ここでのアルカリ性貯液槽6は、処理水受け具7用に箱形容器B1を区画化して一部を割り当てた後の箱形容器B1の残り全てが供された受槽である。隣接配置される処理水受け具7側の立板部60の高さを他部分より一段低く設定する。アルカリ性貯液槽6から処理水受け具7へのアルカリ性廃液YLの流れは、図2に示すようにアルカリ性廃液YLの液面YL1が前記立板部60のレベルを超えたとき、オーバーフローして流れ出すようにしている。
アルカリ性貯液槽6の底板部61には、透析終了後の消毒,洗浄で発生する廃液のうち、アルカリ性廃液YLをアルカリ性貯液槽6に導くアルカリ性廃液分岐管YPの開口YP0が設けられる。アルカリ性廃液分岐管YPの開口先端部は底板部61から若干上方に向け突出する。開口YP0は図1,図2のごとくアルカリ性廃液分岐管YP側の立板部60寄りの底板部61に設けられる。
一方、処理水受け具7側の立板部60寄りのアルカリ性貯液槽6内には隔板64が起立して槽内を分割している。アルカリ性貯液槽6内は、アルカリ性廃液YLがエアバブリングによって中和処理される処理本体部6aと、隔板64によって隔てられ中和処理された処理水が一旦溜まる処理済み部6bと、に分けられる。アルカリ性貯液槽6内のアルカリ性廃液YLが中和処理され、その処理水を水供給具9で処理水受け具7へと押し流す際、処理水と水道水とを効率良く置換して押し流すことができるからである。隔板64の下縁と底板部61とは必要長さ分だけ離れ、また図2のごとく隔板64の上縁は処理水受け具7との境になっている立板部60の上縁より上方に突出する。
そして、アルカリ性貯液槽6の槽内(特に処理本体部6a内)に、詳細を後述するエアバブリング発生器82が設置される構成とする。アルカリ性貯液槽6は該エアバブリング発生器から気泡gが発生することで、次亜塩素酸ナトリウム等のアルカリ性廃液YLを中和処理できる処理槽になっている。
The alkaline storage tank 6 is an alkaline waste liquid dedicated tank having a top plate portion 60 and a bottom plate portion 61 and forming a box-type receiving tank with an open top surface. For example, alkaline waste liquid for one day generated by disinfection and washing after dialysis is completed. Has enough capacity to accept YL. Here, the alkaline liquid storage tank 6 is a receiving tank in which all of the remainder of the box-shaped container B1 after the box-shaped container B1 is partitioned and partially allocated for the treated water receptacle 7 is provided. The height of the standing plate portion 60 on the side of the treated water receiver 7 that is disposed adjacently is set to be one step lower than the other portions. The flow of the alkaline waste liquid YL from the alkaline liquid storage tank 6 to the treated water receptacle 7 overflows and flows out when the level YL1 of the alkaline waste liquid YL exceeds the level of the vertical plate portion 60 as shown in FIG. I am doing so.
The bottom plate portion 61 of the alkaline liquid storage tank 6 is provided with an opening YP0 of the alkaline waste liquid branch pipe YP that guides the alkaline waste liquid YL to the alkaline liquid storage tank 6 out of the waste liquid generated by disinfection and washing after dialysis. The opening front end portion of the alkaline waste liquid branch pipe YP protrudes slightly upward from the bottom plate portion 61. As shown in FIGS. 1 and 2, the opening YP0 is provided in the bottom plate portion 61 near the standing plate portion 60 on the alkaline waste liquid branch pipe YP side.
On the other hand, a partition plate 64 stands up in the alkaline liquid storage tank 6 near the standing plate portion 60 on the treated water receiver 7 side to divide the inside of the tank. The alkaline storage tank 6 is divided into a treatment body 6a where the alkaline waste liquid YL is neutralized by air bubbling and a treated portion 6b where the neutralized treated water separated by the partition plate 64 is temporarily stored. It is done. When the alkaline waste liquid YL in the alkaline liquid storage tank 6 is neutralized and the treated water is pushed to the treated water receptacle 7 by the water supply tool 9, the treated water and tap water can be efficiently replaced and washed away. Because it can. The lower edge of the partition plate 64 and the bottom plate portion 61 are separated by a necessary length, and the upper edge of the partition plate 64 is the upper edge of the standing plate portion 60 that is a boundary with the treated water receptacle 7 as shown in FIG. It protrudes further upward.
And it is set as the structure by which the air bubbling generator 82 mentioned later for details is installed in the tank (especially in the process main-body part 6a) of the alkaline liquid storage tank 6. FIG. The alkaline liquid storage tank 6 is a treatment tank that can neutralize alkaline waste liquid YL such as sodium hypochlorite by generating bubbles g from the air bubbling generator.

処理水受け具7は、アルカリ性廃液YLが前記アルカリ性貯液槽6で中和処理された処理水を受け取り、その処理水をアルカリ性廃液の処理水配管YSPへ導く仲介受け具である。本処理水受け具7は前記酸性中和装置Aに設けた処理水受け具と同様、コーン状漏斗とし、アルカリ性貯液槽6の下流側(図2ではアルカリ性貯液槽6の右側)に隣接配置される。処理水受け具7の上縁をアルカリ性貯液槽6に係る下流側の立板部60の外壁に当接させると共に、箱形容器B1を形成する補強立板部f2に当接させて、アルカリ性貯液槽6から流れ出る処理水を確実に捕捉する。処理水受け具7の下部はアルカリ性廃液の処理水配管YSPにつながり、アルカリ性廃液分岐管YPから取り込まれたアルカリ性廃液YLがアルカリ性貯液槽6,処理水受け具7を経由して該処理水配管YSPに送られるようになっている。 The treated water receptacle 7 is a mediator receptacle that receives treated water obtained by neutralizing the alkaline waste liquid YL in the alkaline storage tank 6 and guides the treated water to the treated water pipe YSP of the alkaline waste liquid. The treated water receptacle 7 is a cone-shaped funnel similar to the treated water receptacle 3 provided in the acid neutralizer A, and is located downstream of the alkaline reservoir 6 (on the right side of the alkaline reservoir 6 in FIG. 2). Adjacent to each other. The upper edge of the treated water receptacle 7 is brought into contact with the outer wall of the downstream standing plate portion 60 of the alkaline liquid storage tank 6 and is brought into contact with the reinforcing standing plate portion f2 forming the box-shaped container B1 so as to be alkaline. The treated water flowing out from the liquid storage tank 6 is reliably captured. The lower part of the treated water receptacle 7 is connected to a treated water pipe YSP for alkaline waste liquid, and the alkaline waste liquid YL taken in from the alkaline waste liquid branch pipe YP passes through the alkaline storage tank 6 and treated water receptacle 7 to the treated water pipe. It is sent to YSP.

エアバブリング供給具8はエアポンプ80と送気管81とエアバブリング発生器82とを備える。エアポンプ80は送気管81を介してアルカリ性貯液槽6の底板部61近くの槽内に設置されるエアバブリング発生器82につながる。本実施形態のエアバブリング発生器82は、図2,図3のごとくループ管に多数の小さな透孔821を穿設したものである。該ループ管に送気管81を接続し、エアポンプ80から取り入れたエアが前記透孔821から無数の気泡gとなって上昇し、すなわちアルカリ性貯液槽6内に溜まったアルカリ性廃液YL中を無数の気泡gが上昇し、該アルカリ性廃液YLを中和処理できるようになっている。本実施形態のエアバブリング発生器82は大半が処理本体部6aの領域に水平配置されるが、その一部は処理済み部6bにまで及んでいる。アルカリ性貯液槽6に一旦溜められるアルカリ性廃液YLに関しては、先ず処理本体部6aと処理済み部6bとのわけへだてなくエアバブリングし中和処理させる方が効果的だからである。
前記エアポンプ80は透析液供給装置TKのプログラム信号に対応させることもできるが、一日中稼動させておいてもよい。
The air bubbling supply tool 8 includes an air pump 80, an air supply pipe 81, and an air bubbling generator 82. The air pump 80 is connected to an air bubbling generator 82 installed in a tank near the bottom plate portion 61 of the alkaline liquid storage tank 6 through an air supply pipe 81. The air bubbling generator 82 of this embodiment is one in which a large number of small through holes 821 are formed in a loop pipe as shown in FIGS. The air pipe 81 is connected to the loop pipe, and the air taken in from the air pump 80 rises as countless bubbles g from the through-holes 821, that is, countlessly in the alkaline waste liquid YL accumulated in the alkaline storage tank 6. The bubble g rises so that the alkaline waste liquid YL can be neutralized. Most of the air bubbling generator 82 of the present embodiment is horizontally arranged in the region of the processing main body 6a, but a part thereof extends to the processed portion 6b. This is because the alkaline waste liquid YL once stored in the alkaline liquid storage tank 6 is more effective if it is neutralized by air bubbling without first treating the processing body 6a and the processed part 6b.
The air pump 80 can correspond to the program signal of the dialysate supply device TK, but may be operated all day.

ところで、透析終了後の消毒,洗浄で発生するアルカリ性廃液YLは次亜塩素酸ナトリウム水溶液等のアルカリ性廃液YLであることが多い。本発明者は、この次亜塩素酸ナトリウム含有廃液からなるアルカリ性廃液YLを薬剤を使用することなく中和処理ができる方法がないか鋭意研究を重ね、アルカリ性貯液槽6内にエアバブリング発生器82を設けてエアバブリングさせることによって比較的容易に且つ実用上問題が発生しない数時間で中和処理できることを見い出した。エアバブリングさせることによって次亜塩素酸ナトリウム等のアルカリ性廃液YLを中和処理できるその理由は定かでないが、例えば次のようなことが想定される。
次亜塩素酸ナトリウムは温度や直射日光により経時変化を起こすといわれているが、エアバブリングでも時間(具体的には3時間以上)をかければ次亜塩素酸ナトリウムが分解し、そのアルカリ性廃液YLのpH値が下がると考えられる。あるいは、エアバブリング過程で、空気中の在る成分が次亜塩素酸ナトリウムに作用してpH値を下げるものと考えられる。いずれにせよ、エアバブリング処理時間として実用上問題にならない数時間かけるだけで、次亜塩素酸ナトリウム含有廃液からなるアルカリ性廃液YLのpH値が下がるのを実験確認している。
By the way, the alkaline waste liquid YL generated by disinfection and washing after completion of dialysis is often an alkaline waste liquid YL such as an aqueous sodium hypochlorite solution. The present inventor has earnestly studied whether there is a method capable of neutralizing the alkaline waste liquid YL composed of this sodium hypochlorite-containing waste liquid without using a chemical, and an air bubbling generator in the alkaline storage tank 6. It has been found that neutralization can be carried out relatively easily and in a few hours without causing any practical problems by providing 82 and air bubbling. The reason why the alkaline waste liquid YL such as sodium hypochlorite can be neutralized by air bubbling is not clear, but the following is assumed, for example.
Sodium hypochlorite is said to change over time due to temperature and direct sunlight, but even if air bubbling takes time (specifically 3 hours or more), sodium hypochlorite decomposes and its alkaline waste liquid YL It is considered that the pH value of Alternatively, in the air bubbling process, components present in the air are considered to act on sodium hypochlorite to lower the pH value. In any case, it has been experimentally confirmed that the pH value of the alkaline waste liquid YL composed of the sodium hypochlorite-containing waste liquid is lowered only by taking several hours as an air bubbling treatment time, which is not a practical problem.

水供給具9は水をアルカリ性貯液槽6に水を送り込む器具である。ここでは、酸性中和装置Aの水供給具と同様、水道管につなげる接続配管91と、水の制御用コンピュータ92と酸性貯液槽1内に水道水を導入する導入管93とからなる。
水の制御用コンピュータとして潅水コンピュータ92を採用し、潅水コンピュータ92で適切な時刻を選定して間欠運転を行う。導入管93はその先端部がアルカリ性貯液槽6内の隔板64寄りの前記処理本体部6aに配され、底板部61近くで先端ノズル931がアルカリ性廃液分岐管YPの導入側にノズル口を向けて設置される。潅水コンピュータ92で制御されて水道水が間欠的に先端ノズル931から噴出する。該水道水の水圧を利用して、処理本体部6a(アルカリ性貯液槽6)内でアルカリ性廃液YLの中和処理を終えた処理水を循環させ、順次、該処理水を隔板64を潜らせ処理部へと送り、その後、処理済み部6bから立板部60の堰を乗り越え、オーバフローさせて処理水受け具7へと流出させることができる。
The water supply tool 9 is an instrument that feeds water into the alkaline liquid storage tank 6. Here, similarly to the water supply tool 5 of the acid neutralizer A, the connection pipe 91 is connected to a water pipe, a water control computer 92 and an introduction pipe 93 for introducing tap water into the acidic liquid storage tank 1. .
An irrigation computer 92 is employed as the water control computer, and intermittent operation is performed by selecting an appropriate time with the irrigation computer 92. The leading end of the introduction pipe 93 is disposed in the processing main body 6a near the partition plate 64 in the alkaline liquid storage tank 6, and the tip nozzle 931 near the bottom plate 61 has a nozzle opening on the introduction side of the alkaline waste liquid branch pipe YP. Installed. Controlled by the irrigation computer 92, tap water is intermittently ejected from the tip nozzle 931. Utilizing the water pressure of the tap water, the treated water after the neutralization treatment of the alkaline waste liquid YL is circulated in the treatment main body 6a (alkaline storage tank 6), and the treated water is sequentially hidden through the partition plate 64. It can be sent to the wastewater treatment part, and then it can get over the weir of the upright plate part 60 from the treated part 6b, overflow and flow out to the treated water receptacle 7.

(3)中和処理装置の周辺設備
本中和処理装置では、周辺設備として透析終了後の消毒,洗浄で発生する廃液を、酸性貯液槽1へ移送する配管XPとアルカリ性貯液槽6へ移送する配管YPと一般下水道へ移送する一般放流配管MPとに分岐してなる3系統の配管と、これら3系統の配管それぞれに前記廃液を送液できるよう切替え可能な切替バルブXV,YV,MVと、該切替バルブを開閉制御する制御盤CPを備える。
(3) Peripheral equipment of the neutralization treatment apparatus In this neutralization treatment equipment, the waste liquid generated by disinfection and washing after dialysis as peripheral equipment is transferred to the acidic storage tank 1 and the alkaline storage tank 6. Three lines of piping branched into a pipe YP to be transferred and a general outlet pipe MP 2 to be transferred to a general sewer, and switching valves XV, YV, which can be switched so that the waste liquid can be fed to each of these three lines. An MV and a control panel CP that controls opening and closing of the switching valve are provided.

本実施形態は透析終了後の消毒,洗浄で発生する廃液を運ぶメイン廃液本管MPから枝管の酸性廃液分岐管XPが分岐し、該酸性廃液分岐管XPの先端が酸性貯液槽1に接続されるが、酸性廃液分岐管XPの途中に電磁弁XVが組み込まれている。
また、メイン廃液本管MPから枝管のアルカリ性廃液分岐管YPが分岐し、該アルカリ性廃液分岐管YPの先端がアルカリ性貯液槽6に接続されるが、アルカリ性廃液分岐管YPの途中には電磁弁YVが組み込まれている。
メイン廃液本管MPにはアルカリ性廃液分岐配管YP,酸性廃液分岐配管XPの分岐地点を過ぎた下流箇所で本管用電磁弁MVが組み込まれる。該本管用電磁弁MVの下流側に一般放流配管MPが接続されて、その先は一般下水道につながる。
In this embodiment, the acidic waste liquid branch pipe XP of the branch pipe branches from the main waste liquid main pipe MP 1 carrying the waste liquid generated by disinfection and washing after dialysis, and the tip of the acidic waste liquid branch pipe XP is the acidic liquid storage tank 1. The electromagnetic valve XV is incorporated in the middle of the acidic waste liquid branch pipe XP.
Also, branches alkaline waste liquid branch pipe YP of the lateral pipe from the main effluent mains MP 1, but the tip of the alkaline waste liquid branch pipe YP are connected to an alkaline reservoir 6, in the middle of the alkaline waste liquid branch pipe YP is A solenoid valve YV is incorporated.
Alkaline waste branch pipe YP to the main waste liquid main pipe MP 1, main solenoid valve MV is incorporated in downstream locations past the junction of the acidic waste liquid branch pipe XP. Generally discharge pipe MP 2 is connected to the downstream side of the solenoid valve MV for the main tube, ahead it leads to generally sewer.

制御盤CPは透析液供給装置TKの透析プログラム設定データを検知して各電磁弁を開閉し、透析終了後の消毒,洗浄で発生する廃液のうち、酸性廃液XLを酸性貯液槽1へ導き、アルカリ性廃液YLはアルカリ性貯液槽6へ導き、また水洗排水は一般放流配管MPへと導くコントローラである。例えば、酸洗浄によって酸性廃液XLがメイン廃液本管MP内を流れる場合は、電磁弁YV,MVが閉、電磁弁XVが開となってその酸性廃液XLを酸性貯液槽1へと導く。次亜塩素酸ナトリウム等の薬洗によってアルカリ性廃液YLがメイン廃液本管MP内を流れる場合は、電磁弁XV,MVが閉、電磁弁YVが開となってそのアルカリ性廃液YLをアルカリ性貯液槽6へと導く。RO水洗等によって水洗排水がメイン廃液本管内を流れる場合は、電磁弁YV,XVが閉、電磁弁MVが開となってその水洗排水を一般放流配管MPへと導く。The control panel CP detects the dialysis program setting data of the dialysate supply device TK, opens and closes each solenoid valve, and guides the acidic waste liquid XL to the acidic storage tank 1 out of the waste liquid generated by disinfection and washing after dialysis. , alkaline waste YL lead to an alkaline storage tank 6. the rinsing waste water is a controller lead to general discharge pipe MP 2. For example, when the acidic waste liquid XL flows through the main waste liquid main pipe MP 1 by acid cleaning, the electromagnetic valves YV and MV are closed and the electromagnetic valve XV is opened to guide the acidic waste liquid XL to the acidic storage tank 1. . If alkaline waste YL by chemical washing of sodium hypochlorite or the like flows through the main waste main pipe MP 1, the solenoid valve XV, MV is closed, alkaline the alkaline waste YL become solenoid valve YV is open reservoir Guide to tank 6. When flowing through the main waste present tract washing wastewater by RO water washing or the like, an electromagnetic valve YV, XV is closed, so the solenoid valve MV is opened leads the washing water discharge into the general discharge pipe MP 2.

(4)透析機器の洗浄,消毒廃液の中和処理方法
上記中和処理装置を用い、例えば次のようにして透析機器の洗浄,消毒廃液の中和処理を行うことができる。
まず、透析中の廃液、及び透析機器の洗浄,消毒廃液のうちで例えば水洗−酸洗浄−水洗−薬洗−水洗といった工程中の水洗排水は、pH値が水質基準内に入っていることから、本中和処理装置に取り込まずに下水道に直接放流する。このとき、切替弁XV,YVは閉で、切替弁MVが開になっている。
(4) Dialysis equipment cleaning and disinfection waste solution neutralization method The neutralization treatment method can be performed, for example, in the following manner using the above neutralization apparatus.
First, among waste liquids during dialysis, and dialysis equipment cleaning and disinfecting waste liquids, for example, water drainage in the process of water washing, acid washing, water washing, chemical washing, and water washing has a pH value within the water quality standard. Discharge directly into the sewer without taking it into the neutralizer. At this time, the switching valves XV and YV are closed and the switching valve MV is open.

そして、酸性廃液XLが排出される時間帯は、制御盤CPが透析液供給装置TKからの信号指令を受けて電磁弁XVを開にし且つ電磁弁YV,MVを閉にして、酸性廃液XLがメイン排水本管から酸性廃液分岐管XPを通って酸性中和装置Aに入るようにする(図4の破線矢印)。  During the time period when the acidic waste liquid XL is discharged, the control panel CP receives a signal command from the dialysate supply device TK, opens the electromagnetic valve XV, and closes the electromagnetic valves YV and MV. The acid neutralizer A is entered from the main drain main pipe through the acidic waste liquid branch pipe XP (broken line arrow in FIG. 4).

また、制御盤CPが、透析液供給装置TKの透析プログラム設定に追従して、アルカリ廃液YLが排出される時間帯は電磁弁YVを開にし且つ電磁弁XV,MVを閉にして、アルカリ性廃液YLがメイン排水本管からアルカリ性廃液分岐管YPを通ってアルカリ性中和装置Bに入るようにする(図2の破線矢印)。  Further, the control panel CP follows the dialysis program setting of the dialysate supply device TK, and during the time period when the alkaline waste liquid YL is discharged, the solenoid valve YV is opened and the solenoid valves XV and MV are closed, so that the alkaline waste liquid YL is allowed to enter the alkaline neutralizer B from the main drainage main pipe through the alkaline waste liquid branch pipe YP (broken arrow in FIG. 2).

酸性中和装置Aに入った前記酸性廃液XLは、まず酸性貯液槽1に一旦溜める。酸性貯液槽1の貯溜量は、透析装置の数量、消毒時間及び洗浄時間によって決められている。
酸性貯液槽1中の酸性廃液XLは、タイマーセットされた水供給具5からの水の噴出により、順次、酸中和槽2へと送られる。先端ノズル531からの水道水の水圧を利用して、酸性貯液槽1に溜まった酸性廃液XLを循環させて酸中和槽2へ送り出していく。酸中和槽2に入った酸性廃液XLは、水酸化マグネシウム等の粒状物4aからなる固形中和剤4が充填された充填層を通過することになる。そして、酸性廃液XLが酸中和槽2の充填層を通過する間に、酸性廃液XLと中和剤4との固液中和反応によってpH値が下がっていく。立板部20や仕切板23或いは隔板24によって形成された4つの筒部(4室)内の充填層を通過する間に、pH値が下水道法等の排出基準値内に整えられる処理水となる。
続いて、水道水の水量が加わったことで、処理水は処理水受け具3との立板20の堰を乗り越え、処理水受け具3へと押し流される。その後、酸性処理水配管XSPを経て、透析中に出る他の廃水に混ざって放流される。
The acidic waste liquid XL that has entered the acidic neutralizer A is first temporarily stored in the acidic liquid storage tank 1. The storage amount of the acidic liquid storage tank 1 is determined by the number of dialysis machines, the disinfection time, and the cleaning time.
The acidic waste liquid XL in the acidic liquid storage tank 1 is sequentially sent to the acid neutralization tank 2 by the ejection of water from the water supply tool 5 set as a timer. Using the water pressure of tap water from the tip nozzle 531, the acidic waste liquid XL accumulated in the acidic liquid storage tank 1 is circulated and sent out to the acid neutralization tank 2. The acidic waste liquid XL that has entered the acid neutralization tank 2 passes through the packed bed filled with the solid neutralizing agent 4 made of particulate matter 4a such as magnesium hydroxide. And while acidic waste liquid XL passes the packed bed of the acid neutralization tank 2, pH value falls by solid-liquid neutralization reaction of acidic waste liquid XL and the neutralizing agent 4. FIG. Treated water whose pH value is adjusted within the discharge standard value such as the sewerage method while passing through the filling layers in the four cylinder portions (four chambers) formed by the standing plate portion 20, the partition plate 23 or the partition plate 24 It becomes.
Subsequently, when the amount of tap water is added, the treated water gets over the weir of the standing plate 20 with the treated water receiver 3 and is washed away to the treated water receiver 3. Then, it is discharged by being mixed with other waste water discharged during dialysis via the acidic treated water pipe XSP.

一方、アルカリ性中和装置Bに入った前記アルカリ性廃液YLは、まずアルカリ性貯液槽6に一旦溜める。アルカリ性貯液槽6の貯溜量も、透析装置の数量、消毒時間及び洗浄時間によって決められる。例えば30ベッドほどある病院の人工透析に係る透析機器の洗浄,消毒廃液は、3t/日程度でその半分がアルカリ性廃水になっている。
アルカリ性貯液槽6にアルカリ性廃液YLが溜められると、エアポンプ80が稼動してエアバブリング発生器82からの気泡gでアルカリ性廃液YL中の次亜塩素酸ナトリウムを時間をかけて分解し、アルカリ性廃液YLのpH値を下水道法等で定める基準値内におさまるよう下げていく。尚、前記エアポンプ80は常時作動させておいてもよい。
このように数時間かけて処理されたアルカリ性廃液YLの処理水は、例えば翌日の透析時間帯にタイマーセットされた水供給具9からの水の噴出により、順次、処理本体部6aを潜って処理済み部6bへと送られ、さらに、処理水受け具7との立板60の堰を乗り越え、処理水受け具7へと押し流される。その後、アルカリ性処理水配管YSPを経て、例えば翌日の透析中に出る他の廃水に混ざって放流される。
On the other hand, the alkaline waste liquid YL that has entered the alkaline neutralizer B is first temporarily stored in the alkaline storage tank 6. The amount of storage in the alkaline liquid storage tank 6 is also determined by the number of dialysis machines, disinfection time, and cleaning time. For example, about 30 tons of washing and disinfecting waste liquid for dialysis equipment related to artificial dialysis in a hospital with about 30 beds, half of which is alkaline waste water.
When the alkaline waste liquid YL is stored in the alkaline liquid storage tank 6, the air pump 80 is operated to decompose sodium hypochlorite in the alkaline waste liquid YL over time with the bubbles g from the air bubbling generator 82, and the alkaline waste liquid. The pH value of YL is lowered so that it falls within the standard value defined by the Sewerage Law. The air pump 80 may be always operated.
The treated water of the alkaline waste liquid YL treated over several hours in this way is treated by, for example, sequentially diving through the treatment main body 6a by the ejection of water from the water supply tool 9 set in the dialysis time zone on the next day. It is sent to the finished portion 6 b, and further gets over the weir of the standing plate 60 with the treated water receptacle 7 and is washed away to the treated water receptacle 7. After that, it is discharged through the alkaline treated water pipe YSP, for example, mixed with other waste water discharged during dialysis on the next day.

(5)実施例
[実施例1]
・酸性廃液の中和処理試験
図4に示すような1500mm×300mm×900mmのステンレス製箱形容器Aに立板部で分離された370mm×300mm×700mmの酸性貯液槽1と、300mm×300mm×650mmと300mm×300mm×600mmとに二分された酸中和槽2とを備える酸性中和装置Aを使用した。水酸化マグネシウム又は酸化マグネシウムを主成分とする粒状物で、その粒径が3mm〜5mmのものを選別してこれを中和剤4とし、該中和剤4については90kgと80kgとを二分された前記酸中和槽2の網状体25上に充填し、酸性中和装置Aを完成させた。
そして、酸性貯液槽1及び酸中和槽2内を1%酢酸溶液で満たした。次いで、5000ml/分で同じ1%酢酸溶液を酸性貯溜槽に流入させた。この使用した1%酢酸溶液のpH値は2.8であった。酸中和槽2を経由した酸性廃液XLのpH値は5.3となり、中和作用,効果が得られた。
(5) Example [Example 1]
Acidic waste liquid neutralization test As shown in FIG. 4, a 1500 mm × 300 mm × 900 mm stainless steel box A 1 370 mm × 300 mm × 700 mm acidic storage tank 1 separated by a standing plate portion, and 300 mm × An acid neutralizer A comprising an acid neutralization tank 2 divided into 300 mm × 650 mm and 300 mm × 300 mm × 600 mm was used. A granular material mainly composed of magnesium hydroxide or magnesium oxide and having a particle diameter of 3 mm to 5 mm is selected and used as a neutralizing agent 4. The neutralizing agent 4 is divided into 90 kg and 80 kg. The acid neutralization apparatus A was completed by filling the mesh body 25 of the acid neutralization tank 2.
Then, the acid storage tank 1 and the acid neutralization tank 2 were filled with a 1% acetic acid solution. The same 1% acetic acid solution was then flowed into the acidic reservoir at 5000 ml / min. The pH value of the 1% acetic acid solution used was 2.8. The pH value of the acidic waste liquid XL that passed through the acid neutralization tank 2 was 5.3, and a neutralizing action and an effect were obtained.

[実施例2]
・アルカリ性廃液の中和処理試験
図2に示すようなアルカリ性中和装置Bを用いた。500mm×300mm×500mmのステンレス製アルカリ性貯液槽6に、エアポンプ80から送気管81を経由してエアバブリング発生器82にエアを送り、小さな多数の透孔821から気泡gを放出(エアレーション)させ、アルカリ性廃液YLの中和試験を行った。気象条件は気温8℃、水温5℃であった。エアポンプ80は吐出風量40リットル/分のものを使用した。アルカリ性貯液槽6を01%次亜塩素酸ナトリウム溶液で満たした。エアレーション前のpH値は11.7であった。エアレーションを3時間行ったところpH値は8.2〜8.4となり、中和作用,効果が得られた。
[Example 2]
-Neutralization test of alkaline waste liquid An alkaline neutralizer B as shown in FIG. 2 was used. Air is sent from the air pump 80 to the air bubbling generator 82 through the air supply pipe 81 to the 500 mm × 300 mm × 500 mm stainless alkaline storage tank 6 to release (aerate) the bubbles g from a large number of small through holes 821. The neutralization test of the alkaline waste liquid YL was performed. The weather conditions were an air temperature of 8 ° C and a water temperature of 5 ° C. An air pump 80 having a discharge air volume of 40 liters / minute was used. Alkaline reservoir 6 was filled with a 01% sodium hypochlorite solution. The pH value before aeration was 11.7. When aeration was carried out for 3 hours, the pH value was 8.2 to 8.4, and a neutralizing action and effect were obtained.

(5)本実施形態の効果
このように構成した中和処理装置は、透析終了後に例えば水洗,酸洗浄,薬洗,水洗といった工程を経る透析機器の消毒,洗浄がなされることによって出る廃水のうち、酸洗浄で出る酸廃液XLを酸性中和装置Aに取り込んで中和処理し、また薬洗で出る次亜塩素酸ナトリウム等のアルカリ性廃液YLをアルカリ性中和装置Bに取り込んで中和処理することで、廃水処理量を減らし、且つ酸,アルカリを個別処理できるので効率的且つ有効な中和処理ができる。
(5) Effects of the present embodiment The neutralization apparatus configured as described above is a wastewater produced by sterilization and cleaning of a dialysis device that undergoes, for example, water washing, acid washing, chemical washing, and water washing after completion of dialysis. Among them, the acid waste liquid XL produced by acid washing is taken into the acid neutralizer A and neutralized, and the alkaline waste liquid YL such as sodium hypochlorite produced by chemical washing is taken into the alkaline neutralizer B and neutralized. By doing so, the amount of wastewater treated can be reduced, and acid and alkali can be individually treated, so that an efficient and effective neutralization treatment can be performed.

次亜塩素酸ナトリウムは毒性が強く微生物を死滅させる虞れがあるが、次亜塩素酸ナトリウムが分解し、アルカリ性廃液YLが中和無害化するので、そのような心配はいらなくなる。またアルカリ性廃液YLの処理はエアバブリング発生器82で、すなわち空気の気泡gで処理するので、薬剤等がいらず、低コストにして環境にも優しいアルカリ性中和装置B(中和処理装置)になる。次亜塩素酸ナトリウム等のアルカリ性廃液YLはアルカリ性中和装置Bに導いて個別処理するので、酸性廃液XLと混ざることによって塩素等の有害ガスが発生する事態も回避でき、安全性が確保される。  Sodium hypochlorite is highly toxic and may kill microorganisms. However, since sodium hypochlorite is decomposed and the alkaline waste liquid YL is neutralized and detoxified, such a worry is eliminated. Further, since the alkaline waste liquid YL is treated with the air bubbling generator 82, that is, with the air bubbles g, the alkaline neutralizer B (neutralizer) is free of chemicals and is low in cost and friendly to the environment. Become. Since the alkaline waste liquid YL such as sodium hypochlorite is individually treated by being guided to the alkaline neutralizer B, it is possible to avoid the occurrence of harmful gases such as chlorine by mixing with the acidic waste liquid XL, and safety is ensured. .

そして、pH値に問題のない水洗排水はそのまま一般下水道に放流することで、例えば一日分を溜める酸性貯液槽1やアルカリ性貯液槽6も比較的小容量になり中和処理装置の設置スペースを小さくできる。これまで設置場所の確保が困難で導入が難しかった病院等でも本中和処理装置の設備導入がし易くなっている。加えて、本実施形態は箱形容器A,Bを一体化して中和処理装置をコンパクト化するので設置スペースが一層小さくなり優れたものになっている。Then, flush wastewater having no problem in pH value is discharged into the general sewer as it is, and for example, the acid storage tank 1 and the alkaline storage tank 6 for storing a day's worth become relatively small in volume, and the neutralization apparatus is installed. Space can be reduced. Even in hospitals where it has been difficult to secure the installation location so far, it is easy to introduce the neutralization treatment equipment. In addition, since the neutralization apparatus is made compact by integrating the box-shaped containers A 1 and B 1 in this embodiment, the installation space is further reduced and the apparatus is excellent.

また、酸性処理装置Aにあっては、中和剤4に水に溶解してアルカリを呈する前記粒状物4aが水酸化マグネシウム又は酸化マグネシウムを主成分とする粒状物を用いているので、天然岩石粒子等に比べ中和反応が速く、また酸中和槽2に充填する量も少なくて済む。さらに、海水法水酸化マグネシウムからなる中和剤4を用いると、粒子を大きくして沈降性,濾過性の良い水酸化マグネシウム主成分の中和剤が得られることから、酸中和処理中にアクが出ず、且つ粒径も適度な大きさで、作業性,取扱いに優れたものとなる。  Moreover, in the acidic processing apparatus A, since the said granular material 4a which melt | dissolves in water in the neutralizing agent 4 and exhibits an alkali uses the granular material which has magnesium hydroxide or magnesium oxide as a main component, natural rock Compared with particles and the like, the neutralization reaction is fast, and the amount to be filled in the acid neutralization tank 2 is small. Furthermore, when the neutralizing agent 4 made of seawater-processed magnesium hydroxide is used, the particles can be enlarged to obtain a neutralizing agent containing magnesium hydroxide as a main component with good sedimentation and filterability. It is excellent in workability and handling because it is free from agitation and has an appropriate particle size.

尚、本発明においては、前記実施形態,実施例に示すものに限られず、目的,用途に応じて本発明の範囲で種々変更できる。酸性中和装置A,酸性貯液槽1,酸中和槽2,処理水受け具3,中和剤4,水供給具5,アルカリ性中和装置B,アルカリ性貯液槽6,処理水受け具7,エアバブリング発生器82,水供給具9等の形状,大きさ,材質等は用途に合わせて本発明の範囲内で適宜選択できる。例えば、透析治療のベッドごとに各ベッドと対にした極く小さな中和処理装置とすることもできる。 The present invention is not limited to those shown in the above-described embodiments and examples, and various modifications can be made within the scope of the present invention depending on the purpose and application. Acid neutralizer A, acid storage tank 1, acid neutralization tank 2, treated water receptacle 3, neutralizer 4, water supply tool 5, alkaline neutralizer B, alkaline storage tank 6, treated water receptacle 7. The shape, size, material and the like of the air bubbling generator 82, the water supply tool 9 and the like can be appropriately selected within the scope of the present invention according to the application. For example, it may be a very small neutralizing apparatus which each bed pair for each bed dialysis treatment.

本発明に係る透析機器の洗浄,消毒廃液の中和処理装置の一形態で、その概略平面図である。  1 is a schematic plan view of one embodiment of a neutralization treatment apparatus for cleaning and disinfecting waste liquid for dialysis equipment according to the present invention. アルカリ性廃液の中和処理装置に係る一部縦断面説明図である。  It is a partial longitudinal cross-section explanatory drawing which concerns on the neutralization processing apparatus of alkaline waste liquid. 図2のエアバブリング供給具の説明斜視図である。  FIG. 3 is an explanatory perspective view of the air bubbling supply tool of FIG. 2. 酸性廃液の中和処理装置に係る一部縦断面説明図である。  It is a partial longitudinal cross-section explanatory drawing which concerns on the neutralization processing apparatus of an acidic waste liquid.

符号の説明Explanation of symbols

1 酸性貯液槽
2 酸中和槽
4 中和剤(水に溶解してアルカリを呈する粒状物)
6 アルカリ性貯液槽
82 エアバブリング発生器
CP 制御盤
XL 酸性廃液
YL アルカリ性廃液
XV 電磁弁(切替バルブ)
YV 電磁弁(切替バルブ)
MV 電磁弁(切替バルブ)
XP 酸性廃液分岐管(配管)
YP アルカリ性廃液分岐管(配管)
MP 一般放流管
DESCRIPTION OF SYMBOLS 1 Acid storage tank 2 Acid neutralization tank 4 Neutralizing agent (The granular material which melt | dissolves in water and exhibits an alkali)
6 Alkaline liquid storage tank 82 Air bubbling generator CP Control panel XL Acid waste liquid YL Alkaline waste liquid XV Solenoid valve (switching valve)
YV solenoid valve (switching valve)
MV solenoid valve (switching valve)
XP Acid waste liquid branch pipe (pipe)
YP Alkaline waste liquid branch pipe (pipe)
MP 2 general discharge pipe

Claims (2)

透析終了後の消毒,洗浄で発生する酸性廃液を受け入れる酸性廃液専用の酸性貯液槽と、水に溶解してアルカリ性を呈する粒状物が槽内に充填された酸中和槽と、を具備し、前記酸性貯液槽に溜めた酸性廃液を前記酸中和槽に送液し中和処理をなすと共に、透析終了後の消毒,洗浄で発生するアルカリ性廃液を受け入れるアルカリ性廃液専用のアルカリ性貯液槽をさらに具備し、アルカリ性廃液を中和処理するようにし、且つ、透析終了後の消毒,洗浄で発生する廃液を、前記酸性貯液槽へ移送する配管と前記アルカリ性貯液槽へ移送する配管と一般下水道へ移送する一般放流配管とに分岐してなる3系統の配管と、これら3系統の配管それぞれに前記廃液を送液できるよう切替え可能な切替バルブと、該切替バルブを開閉制御する制御盤と、を具備することを特徴とする透析機器の洗浄,消毒廃液の中和処理装置。 An acid storage tank dedicated to the acidic waste liquid that receives the acidic waste liquid generated by sterilization and washing after dialysis is completed, and an acid neutralization tank that is filled with granular material that dissolves in water and exhibits alkalinity. , wherein the acidic liquid storage tank to the reservoir and the acidic effluent with to a liquid feed for neutralization in the acid neutralization tank, disinfection after completion of the dialysis, alkaline waste only alkaline reservoir accept alkaline waste liquid generated by washing A pipe for further neutralizing the alkaline waste liquid and transferring the waste liquid generated by disinfection and washing after dialysis to the acidic storage tank and to the alkaline storage tank. And a general discharge pipe that transfers to the general sewer, a three-way pipe, a switching valve that can be switched so that the waste liquid can be sent to each of the three pipes, and a control that controls the opening and closing of the switching valve and the board, the Cleaning of the dialysis apparatus, characterized by Bei, neutralizing apparatus disinfecting waste. 前記アルカリ性貯液槽内にエアバブリング発生器を具備し、次亜塩素酸ナトリウム含有廃液からなるアルカリ性廃液をエアバブリングさせて中和処理するようにした請求項記載の透析機器の洗浄,消毒廃液の中和処理装置。 Comprising air bubbling generator to the alkaline liquid storage tank, cleaning of the dialysis apparatus according to claim 1, wherein which is adapted to neutralization treatment the alkaline waste liquid consisting of sodium-containing waste liquid hypochlorite is air bubbling, disinfecting waste Neutralization treatment equipment.
JP2004066339A 2004-02-08 2004-02-08 Dialysis equipment cleaning, disinfection wastewater neutralization treatment equipment Expired - Fee Related JP4500071B2 (en)

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JP5227537B2 (en) * 2006-05-08 2013-07-03 節夫 小林 Magnesium-based slow dissolving agent for neutralization of dialysis machine washing wastewater
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EP2698177B1 (en) 2012-08-13 2015-01-14 Sorin Group Deutschland GmbH Method for controlling a disinfection status of a temperature control device and temperature control device for human body temperature control during extracorporeal circulation
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JP7492383B2 (en) 2020-06-18 2024-05-29 好夫 久高 Dialysis wastewater neutralization system, control device, dialysis wastewater neutralization method, and dialysis wastewater neutralization program
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JP2001269670A (en) * 2000-03-24 2001-10-02 Nikkiso Co Ltd Neutralization treatment device for waste liquid derived from artificial dialysis
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