JPS60206489A - Method and apparatus for post-treatment of prepared fresh water - Google Patents

Method and apparatus for post-treatment of prepared fresh water

Info

Publication number
JPS60206489A
JPS60206489A JP6480084A JP6480084A JPS60206489A JP S60206489 A JPS60206489 A JP S60206489A JP 6480084 A JP6480084 A JP 6480084A JP 6480084 A JP6480084 A JP 6480084A JP S60206489 A JPS60206489 A JP S60206489A
Authority
JP
Japan
Prior art keywords
limestone
fresh water
carbon dioxide
decomposition
produced
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Granted
Application number
JP6480084A
Other languages
Japanese (ja)
Other versions
JPH0472597B2 (en
Inventor
Satoshi Ihara
井原 郷司
Michio Miura
三浦 三智男
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Sasakura Engineering Co Ltd
Original Assignee
Sasakura Engineering Co Ltd
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Sasakura Engineering Co Ltd filed Critical Sasakura Engineering Co Ltd
Priority to JP6480084A priority Critical patent/JPS60206489A/en
Publication of JPS60206489A publication Critical patent/JPS60206489A/en
Publication of JPH0472597B2 publication Critical patent/JPH0472597B2/ja
Granted legal-status Critical Current

Links

Abstract

PURPOSE:To obtain drinking water having good quality, by guiding a part of prepared fresh water to the side of a limestone decomposition furnace to mix the same with formed quick lime and, thereafter, allowing the resulting mixing to absorb carbon dioxide while mixing the treated water with high purity carbon dioxide from the decomposition furnace and the remaining formed fresh water. CONSTITUTION:An externally heated limestone decomposition furnace 2 is provided in close vicinity to the installation place of the evaporation apparatus 1 of a fresh water making apparatus, for example, a seawater desalting apparatus and distilled water being fresh water formed from an evaporation 3 is introduced into a calcium dissolving apparatus 5 through a pipe 4, because contains only several ppm of TDS and unsuitable for drinking water, to impart hardness. That is, carbon dioxide generated by the decomposition of limestone in the heated decomposition tower 2' of the limestone decomposition furnace 2 keeps high purity and enters the calcium dissolving apparatus 5 to be dissolved in fresh water and CaCO3, H2O and CO2 are reacted in the dissolving apparatus 5 to form Ca(HCO3)2 in a dissolved state and hardness is imparted to fresh water.

Description

【発明の詳細な説明】 本発明は、淡水化装置で得られた生成淡水を水通水に適
した水質に転換するための超小形の石灰石分解炉を備え
た後処理方法および装置に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a post-treatment method and device equipped with an ultra-small limestone decomposition furnace for converting produced fresh water obtained in a desalination device into a water quality suitable for water flow. be.

石灰石の石灰の一部が苦土で入れ替った白雲石(ドロマ
イト)系を含んでも全く同転の反応となるので、本発明
では一部の説明は省略するが、Caで示される部分はす
べてCa十Mqである場合を含むものとする。
Even if some of the lime in limestone contains dolomite (dolomite), which is replaced by magnesia, the reaction will be completely the same, so in this invention, some explanations will be omitted, but all parts indicated by Ca This includes the case where Ca is 10Mq.

淡水化装置によって得られた淡水はミネラル成分を殆ん
ど含んでいないから、以後の給水系統の配管材料を腐食
させ、また飲料水としては味覚に乏しいものであった。
Since the fresh water obtained by the desalination equipment contains almost no mineral components, it corrodes the piping materials of the subsequent water supply system and has a poor taste as drinking water.

これらの欠点を補うため、淡水に炭酸カルシウムや消石
灰と炭酸ガスとを添加して製造水とする方法が採用され
ており、一般には石灰石を充填した容器、いわゆるライ
ムストンフィルターが設置され、これに炭酸ガスを吸収
した淡水が通過して下記反応により炭酸水素カルシウム
が生成し硬度を増す。
In order to compensate for these shortcomings, a method has been adopted to make manufactured water by adding calcium carbonate or slaked lime and carbon dioxide gas to fresh water.Generally, a container filled with limestone, a so-called limestone filter, is installed. Fresh water that has absorbed carbon dioxide gas passes through it, and calcium bicarbonate is produced through the following reaction, increasing hardness.

CaCO3+ )120 + CO2 −+Ca(ト1co、) 2 − ・・−・ (1)こ
のライムストンフィルターには通常入手し易く安価な2
〜20mm粒度の石灰石を充填して使用しているが、多
くの場合純度が低く不純物を含み、また溶解速度が遅く
、硬度が附与されても水質が劣ることもあり、このライ
ムストンフィルターは容量の割に淡水の処理量は低く、
よって大型塩水淡水化装置では該フィルターを数十基も
併設することとなり、設備費が高くなりかつ石灰石は各
フィルターに投入しなければならず、この補充作業は不
溶解スライムの排出作業とともに仲々煩雑であった。
CaCO3+ ) 120 + CO2 −+Ca(To1co,) 2 − ... (1) This limestone filter usually uses easily available and inexpensive 2
Although limestone with a particle size of ~20mm is used, it is often of low purity and contains impurities, has a slow dissolution rate, and even if hardness is imparted, the water quality may be poor, so this limestone filter is The amount of fresh water processed is low compared to the capacity.
Therefore, large-scale salt water desalination equipment must be equipped with dozens of such filters, which increases equipment costs and requires limestone to be added to each filter, making this replenishment work, along with the work of discharging undissolved slime, quite complicated. Met.

一方、炭酸ガスは淡水化装置における海水中の重炭酸成
分の分解抽気により取得できる場合もあるから、これを
使用すれば合理的であるが、その際アンモニア、油分、
臭素等の不純物が含有する危険性があり、また該抽気エ
ゼクター用蒸気のボイラー用脱酸素剤としてヒドラジン
を使用した場 。
On the other hand, carbon dioxide gas can sometimes be obtained by decomposing and extracting bicarbonate components in seawater in desalination equipment, so it would be reasonable to use this method, but in this case, ammonia, oil,
There is a risk of containing impurities such as bromine, and when hydrazine is used as an oxygen scavenger for the boiler of the steam for the extraction ejector.

合、抽気中の炭酸ガスにはヒドラジン等が混入づる恐れ
があり問題である。
In this case, there is a risk that hydrazine or the like may be mixed into the carbon dioxide gas being extracted, which is a problem.

また炭酸ガスの入手は油またはガスを燃焼して生成する
炭酸ガスをエタノールアミンなどの溶剤を使用して回収
するプロセスから取得する方法、あるいは購入液化炭酸
ガスの使用も考えられるが、前者では装置が大規模の場
合と同型式となり複雑となってポンプ等の動力が増大す
るばかりでなく、機器の数も多く建設コストも高価なも
のとなり、保健上も問題が残る。後者は価格(ランニン
グコスト)の高騰を招き実用的でない。即ちこの場合の
数+N]n”/H(CO2どして)程度の要求に対して
、前者は無理なスケールダウンであり、後者では消費量
がやや多過ぎるとともに供給切れの不安をも伴うもので
ある。
In addition, carbon dioxide gas can be obtained through a process in which carbon dioxide gas produced by burning oil or gas is recovered using a solvent such as ethanolamine, or purchased liquefied carbon dioxide gas can be used; The system is of the same type as a large-scale system, making it complicated and requiring more power for pumps, etc., as well as requiring a large number of equipment and increasing construction costs, which also poses health problems. The latter is impractical as it causes a rise in price (running costs). In other words, in this case, the former would be an unreasonable scale-down for the requirement of about number + N]n''/H (CO2 etc.), and the latter would result in slightly too much consumption and the fear of running out of supply. It is.

上記のとおり炭酸ガスの必要量は数十N m’ / l
−1(CO2として)の能力であり、石灰石としてし1
00h/H程度の微々たる取扱数口となり、此の凹に見
合う小径の石灰石を連続的に処理することとなり、工業
規模の数十mmφ以上の石灰石に比して分解時間も桁違
いに短かく、従って滞留量も僅かなものとなり、後記セ
ラミック管などの管内で加熱するに適する程度となるな
ど、従来の石灰炉とは全く概念が異なるため、本発明は
新たに開発した超小型の石灰石分解炉とこれに淡水化装
置とを有機的に組合わせて、若干低品位の石灰石の場合
であっても、より高純度の消石灰溶液または石灰乳を生
成させ、次いでより低純度のIAMガスを利用して先ず
炭酸カルシウムの微粒スラリーを生成させ、更に発生炭
酸ガスを淡水中で該炭酸ツノルシウム微粒と反応させて
炭酸水素カルシウムを効率よく生成させる。即ち上記反
応式(1)の前に下記 Ca (OH)2 + CO2 −+ CaC0z + H20−−−−−−(2)の反
応によって稀薄な炭酸ガスをも捉えC炭酸カルシウムを
生成さけ、該生成炭酸カルシウムに史に淡水と炭酸ガス
を(1)式で反応させ、炭酸水素カルシウムを淡水に溶
解させる方法であって、経済的であり、かつ装置の小型
化連続化、及び水質基準に合格する安定した飲料水の取
得を目的どしてなされたものである。以下本発明を添付
の図面を参照して説明する。
As mentioned above, the required amount of carbon dioxide gas is several tens of N m'/l.
-1 (as CO2), and as limestone
The handling time is only a small number of 00h/h, and the small diameter limestone corresponding to this concavity is continuously processed, and the decomposition time is orders of magnitude shorter than industrial scale limestone with a diameter of several tens of mm or more. Therefore, the retention amount is small, making it suitable for heating inside a pipe such as a ceramic pipe described later.The concept is completely different from that of a conventional lime furnace, so the present invention is a newly developed ultra-small limestone decomposition method. Combining the furnace with a desalination unit organically to produce a higher purity slaked lime solution or milk of lime, even with slightly lower grade limestone, and then utilizing lower purity IAM gas. First, a slurry of fine particles of calcium carbonate is produced, and then the generated carbon dioxide gas is reacted with the fine particles of tunorsium carbonate in fresh water to efficiently produce calcium hydrogen carbonate. That is, before the above reaction formula (1), the following reaction Ca (OH) 2 + CO 2 − + CaC0z + H 20 −−−−−−−−−−−−−−−−−−−−−−−− (2) is performed to capture dilute carbon dioxide gas and to avoid generating C calcium carbonate. This is a method of dissolving calcium bicarbonate in fresh water by reacting the produced calcium carbonate with fresh water and carbon dioxide gas according to equation (1), which is economical, allows for smaller and more continuous equipment, and passes water quality standards. This was done for the purpose of obtaining stable drinking water. The present invention will now be described with reference to the accompanying drawings.

淡水化装置、例えば海水淡水化蒸発装置(1)の設置場
所に近接して外部加熱石灰石分解炉(2ンが設けられて
おり、蒸発器(3)から生成した淡水である蒸留水はT
DSを数ppm Lか含まず、このままでは飲料に適さ
ないので、これを改質するため、管(4)を経て詳細を
後述するカルシウム溶解装置(5)に導入して後記のよ
うに硬度をFI4与する。
An externally heated limestone decomposition furnace (2) is installed close to the installation location of the desalination equipment, for example, the seawater desalination evaporation equipment (1), and the distilled water, which is fresh water produced from the evaporator (3), is
It contains only a few ppm L of DS and is not suitable for drinking as it is, so in order to reform it, it is introduced into the calcium dissolving device (5), which will be described in detail later, through the pipe (4), and the hardness is adjusted as described later. Gives FI4.

一方、拡大して示された石灰石分解炉(2)は外部加熱
方式であって、例えば、カルシウム溶解装置(5)出口
処理水取出管の直径が1000〜1200mmに対応す
る加熱分解塔(2−)には直径は数+m、mと超小形の
管を使用することができ、上部のポツパー(6)から装
入用ダブル弁(7)を経て炉内に装入された数mm程度
の石灰石(8)は、この加熱分解塔(2′)内で例えば
石油を燃料とするバーナーのごとき加熱器(9)によっ
て炉壁(10)を介して900℃以上に加熱され、生石
灰と炭酸ガスに分解し、生石灰は炉下部の冷却ゾーン(
11)を通過する間に、ブロア(12)による空気が流
れる冷却器(13)によって間接冷却されたのち、排出
弁(14)を有する管路(15)を経て下部の生石灰消
化器(16)に落下する。加熱器(9)はバーナー以外
の装置も使用できることは勿論であり、特に小型の場合
は電気を熱源とするのも有利な方法と考えられる。装入
弁(7)及び排出弁(14)にはそれぞれシール機構(
図示せず)を設けて空気の侵入を防ぎ、更に生成炭酸ガ
スの外部への洩れを防ぐため管路(15)にシール用気
体を封入する等の手段がとられるのは勿論であるが、炭
酸ガスの純度を下げることなくシールまたはスイープの
用に供するのは、後の■程で凝縮してしまう水蒸気が特
に好ましい。炉壁の材質としては、耐熱金属たとえばイ
ンコネル、セラミックスとしては例えばSiC,Al1
0J 、その他パイロセラム、サーメット等の耐熱材料
を使用する。
On the other hand, the limestone decomposition furnace (2) shown in an enlarged manner is of an external heating type, and for example, a thermal decomposition tower (2- ) can use ultra-small tubes with diameters of several meters or meters, and limestone of several mm in diameter is charged into the furnace from the top popper (6) through the double charging valve (7). (8) is heated to 900°C or higher through the furnace wall (10) by a heater (9) such as a burner using petroleum as fuel in the thermal decomposition tower (2'), and is converted into quicklime and carbon dioxide gas. The quicklime decomposes into a cooling zone at the bottom of the furnace (
11), the air from the blower (12) is indirectly cooled by the cooler (13) through which it flows, and then passes through the pipe (15) with the discharge valve (14) to the lower quicklime digester (16). to fall. It goes without saying that a device other than a burner can be used as the heater (9), and it is considered advantageous to use electricity as the heat source, especially when the heater is small. The charging valve (7) and the discharge valve (14) each have a sealing mechanism (
Of course, measures such as installing a sealing gas in the pipe (15) to prevent air from entering (not shown) and sealing the pipe (15) to prevent the generated carbon dioxide from leaking to the outside are of course taken. Water vapor, which is condensed in the subsequent step (2), is particularly preferred for use in sealing or sweeping without lowering the purity of carbon dioxide gas. The material for the furnace wall may be a heat-resistant metal such as Inconel, and a ceramic such as SiC or Al1.
0J, other heat-resistant materials such as pyroceram and cermet are used.

生石灰消化器(16)には淡水化装置(1)のカルシウ
ム溶解装置(5)に入る前の淡水が分岐管(17)を経
て装入され、器内で消石灰溶液もしくは石灰乳が生成し
、内部に設けられたシックナー(18)により不純物は
沈泥となって下部(19)より排出され、精製物は管(
20)を経て第1段炭酸ガス吸収器(21)に送出され
る。生石灰消化器(16)は、装入される生石灰の純度
が高いときは容器を用いず長い配管で代用することもで
きる。
The freshwater before entering the calcium dissolving device (5) of the desalination device (1) is charged into the quicklime digester (16) via a branch pipe (17), and slaked lime solution or milk of lime is produced in the device. Impurities are turned into silt by the thickener (18) installed inside and discharged from the lower part (19), and the purified products are discharged through the pipe (19).
20) and is sent to the first stage carbon dioxide absorber (21). In the quicklime digester (16), when the purity of the charged quicklime is high, a long pipe can be used instead of a container.

第1段炭酸ガス吸収塔(21)にはバーナーの燃焼排ガ
スが加熱分解塔(2′)の外周を通りダクト(22)を
経て、熱交換器(23)で管(24)を通過する燃焼用
空気と熱交換して冷却されたのち、管(25)によって
底部(26)に噴出し、排ガス中の炭酸ガスは器内の消
石灰溶液もしくは石灰乳と反応してCaC01を生成す
る。このcacOiは粒径が小さく以後の移送ならびに
反応に好都合となる。余剰の排ガスは上部の管(27)
より大気へ放出さへる。このようにCaCO3生成に低
純度の炭酸ガスが利用できるので経済的である。
In the first stage carbon dioxide absorption tower (21), combustion exhaust gas from the burner passes through the outer periphery of the thermal decomposition tower (2'), passes through the duct (22), and passes through the pipe (24) in the heat exchanger (23). After being cooled by heat exchange with the air, it is ejected to the bottom (26) through a pipe (25), and the carbon dioxide gas in the exhaust gas reacts with the slaked lime solution or milk of lime in the vessel to produce CaC01. This cacOi has a small particle size and is convenient for subsequent transport and reaction. Excess exhaust gas is removed from the upper pipe (27)
It is released more into the atmosphere. In this way, low-purity carbon dioxide gas can be used to generate CaCO3, which is economical.

なお、第1段炭酸ガス吸収器(21)内部には循環水案
内筒(28)を設けて反応を円滑に行わせ菰。
A circulating water guide cylinder (28) is provided inside the first stage carbon dioxide absorber (21) to allow the reaction to occur smoothly.

ここで生成したCa CO3は粒径が小さいからスラリ
ー状となってポンプ(29) 、管(30)を経て流れ
、CaCO3は例えば0.5%程度の濃度でカルシウム
溶解装置(5)に到ってここを通過覆る淡水に混合する
。第1段炭酸ガス吸収器(21)には、上記の燃焼排ガ
ス以外に、一部の石灰石分解ガス、他から得られる炭酸
ガス、例えばボイラ排ガス、海水淡水化装置の抽気ガス
、あるいは空気中の純度の低い炭酸ガスなどを単独もし
くは(71せて利用してもよい。
Since the CaCO3 generated here has a small particle size, it becomes a slurry and flows through the pump (29) and the pipe (30), and the CaCO3 reaches the calcium dissolving device (5) at a concentration of, for example, about 0.5%. It passes through the lever and mixes with the overlying fresh water. In addition to the above-mentioned combustion exhaust gas, the first stage carbon dioxide absorber (21) contains some limestone decomposition gas, carbon dioxide obtained from other sources, such as boiler exhaust gas, bleed gas from a seawater desalination equipment, or in the air. Low-purity carbon dioxide gas or the like may be used alone or in combination.

上記の説明では生成淡水の一部を生石灰消化器(16)
に導入したが、場合によっては管(,4)を省いて生成
淡水の全量を導入してもよい。この場合も石灰石の純度
が良く不純物が殆んどなければ容器(16)を用いず長
い配管で代用することもできる。
In the above explanation, a part of the produced fresh water is transferred to the quicklime digester (16).
However, in some cases, the pipe (, 4) may be omitted and the entire amount of generated fresh water may be introduced. In this case as well, if the limestone is of high purity and contains almost no impurities, the container (16) may be omitted and a long pipe may be used instead.

石灰石分解炉(2)の加熱分解塔(2′)内部で石灰石
の分解によって生じた炭酸ガスは高純度を保ち、管(3
1)を経てカルシウム溶解装置(5)に入り淡水に溶解
し、該溶解装置(5)内でCaCO3、”H20、CO
2が反応してCa (HCo、)、が溶解生成し、淡水
に硬度を附与する、この際、CaCO5は前述のとおり
粒径が小さいので反応速度は大きく、従来のライムスト
ンフィルターのような大規模な装置を必要としない。
The carbon dioxide gas generated by the decomposition of limestone inside the thermal decomposition tower (2') of the limestone decomposition furnace (2) maintains high purity.
1), enters the calcium dissolving device (5) and is dissolved in fresh water, and in the dissolving device (5) CaCO3, “H20, CO
2 reacts, Ca (HCo,) is dissolved and produced, giving hardness to fresh water. At this time, as mentioned above, CaCO5 has a small particle size, so the reaction rate is high, and it cannot be used as a filter like a conventional limestone filter. Does not require large-scale equipment.

管(32)から取出す処理後の淡水に要求される硬度は
炭酸水素イオンとして数十ppm程度であるから、管(
30)ヲ流れる’o、5%程度のCa CO3よりこの
程度の炭酸水素イオンの生成は、使用炭酸ガスの純度が
高く溶解し易いことと相俟って、その反応時間は短かく
なり、かルシウム溶解装置(5)は小形にでき、内部m
構は極めて簡単となり、要は十分混合溶解できるもので
あればよく、簡単な基型式または図示のような配管で適
当な長さをもたせて反応を行わせる炭酸ガス吸収部分〈
33)で十分である。
The hardness required for the treated fresh water taken out from the tube (32) is about several tens of ppm in terms of hydrogen carbonate ions,
30) The production of this amount of hydrogen carbonate ions from about 5% Ca CO3 is possible due to the fact that the carbon dioxide gas used is highly pure and easily soluble, and the reaction time is shortened. The lucium melting device (5) can be made small and the internal m
The structure is extremely simple; all that is required is that it can be sufficiently mixed and dissolved, and the carbon dioxide absorption part is a simple base model or a pipe of an appropriate length as shown in the figure to carry out the reaction.
33) is sufficient.

生成生石灰がその近傍で本後処理以外に一部利用するこ
とができるときには、低純度の炭酸ガスの代りに石灰石
を加熱して発生した高純度炭酸ガスの一部を上記低純度
の代りに使うこともできるが、この部分の炭酸ガス用に
まで石灰石を加熱する熱量だけエネルギー消費が過大と
なり特にその場所で生石灰の少量が常に必要な場合以外
実用的でない。
When a portion of the produced quicklime can be used for purposes other than the main post-treatment in the vicinity, a portion of the high-purity carbon dioxide gas generated by heating the limestone is used instead of the low-purity carbon dioxide gas mentioned above. However, the amount of energy required to heat the limestone to produce carbon dioxide gas in this area would consume too much energy, making it impractical unless a small amount of quicklime is always needed at that location.

本発明は淡水化装置と外部加熱石灰石分解炉とを近傍に
設置して有機的に相互に連絡し、生成淡水の一部または
全部を石灰石分解炉生成生石灰に導いて石灰乳または消
石灰溶液となし、不純物のある場合は一旦沈降分離した
うえで、これに外部加熱石灰石分解炉燃焼排ガス等の純
度の低い炭酸ガス、一部の石灰石分解ガス、他から得た
炭酸ガスを単独もしくは併用して吸収させたのち該炉が
ら発生した高純度炭酸ガスを更に反応させて淡水中に炭
酸水素カルシウムを生成させるから、燃焼排ガス中の低
純度の炭酸ガス等も排棄することなく有効に利用でき、
またカルシウム溶解装置は従来のライムストンフィルタ
ーのように石灰石の充填補充のような断続する煩雑な作
業はなく連続的となるから作業能率は向上できる。炉の
條件また rは加熱器(9)に用いる燃料の種類により
該分解炉のみよりの炭酸ガス量が不足する場合であって
、逆浸透法による淡水化時のように膜の種類により透過
水が炭酸ガスを余り含まないとき、或は近傍に燃焼排ガ
スまたは抽気ガス等の炭酸ガス源のない時には、Ca(
OH)zの強い反応性により、空気中の数百ppmの炭
酸ガスを吸収塔を設けて捕捉して不足分を補うこともで
きる。また燃料中に硫黄分があればCaSO4等となっ
て捕捉された分も有効なカルシウム源となり得る。
The present invention installs a desalination device and an externally heated limestone decomposition furnace in the vicinity, organically communicates with each other, and directs a part or all of the produced fresh water to the quicklime produced in the limestone decomposition furnace to turn it into lime milk or slaked lime solution. If there are impurities, they are first separated by sedimentation, and then low-purity carbon dioxide such as externally heated limestone decomposition furnace combustion exhaust gas, some limestone decomposition gas, and carbon dioxide obtained from other sources are absorbed singly or in combination. After that, the high-purity carbon dioxide gas generated in the furnace is further reacted to produce calcium hydrogen carbonate in fresh water, so low-purity carbon dioxide gas in the combustion exhaust gas can be used effectively without being disposed of.
In addition, unlike conventional limestone filters, the calcium dissolving device does not require intermittent and troublesome work such as filling and replenishing limestone, but can improve work efficiency because it is continuous. The condition of the furnace or r is the case where the amount of carbon dioxide gas from the decomposition furnace alone is insufficient depending on the type of fuel used in the heater (9), and the amount of permeated water is When Ca(
Due to the strong reactivity of OH)z, an absorption tower can be installed to capture several hundred ppm of carbon dioxide gas in the air, thereby making up for the shortage. Further, if there is sulfur in the fuel, the captured sulfur content as CaSO4 etc. can also be an effective source of calcium.

しかも、この炭酸ガスの添加によって粒径の小さいCa
CO3が生成するので以後のカルシウム溶解装置におけ
る溶は易い高純度炭酸ガスとの反応速度は大となる。因
みに数mm程度の石灰石のライムストンフィルターに比
べて本発明の炭酸カルシウム微粒は数百乃至数万倍の比
表面積を有するので該溶@装置は小形で形状は単純化で
き、淡水の通過速度は人となし得゛C処理能力が増大し
、更には配管長に若干のゆとりがあればその一部を利用
する等小形にできるか、または新しい附加設備を省ける
などの効果があり、更に純度の劣る石灰石を原料として
も小粒使用のため運転可能であり、砂の混入した風化貝
殻等も対象として考えられ、また一方炭酸ガスの濃度が
低くても、生成CaCO3は高品位のものに変換でき、
式(2)の反応のところまでは低Fl所の炭酸ガス、極
端な場合は大気さえも使用可能で、式(1)の炭酸ガス
は自給自足できるから、淡水の後処理にd5いて各成分
はバランスがよくとれて無駄がなくなり、淡水化装置の
近くに石灰石採石場があれば、たとえ低品位の石灰石し
か採掘できなくても有効に利用でき、特にその効果は大
である。
Furthermore, the addition of carbon dioxide gas reduces the particle size of Ca.
Since CO3 is generated, the reaction rate with high-purity carbon dioxide gas, which is easy to dissolve, in the subsequent calcium dissolving device increases. Incidentally, since the calcium carbonate fine particles of the present invention have a specific surface area several hundred to tens of thousands of times larger than that of a limestone filter made of limestone with a diameter of several millimeters, the melting device can be small and simple in shape, and the passage speed of fresh water can be reduced. It increases the C processing capacity that can be done by humans, and if there is some extra space in the piping length, it can be made smaller by using part of it, or new additional equipment can be omitted, and the purity can be improved. It is possible to operate even with inferior limestone as a raw material because it uses small particles, and weathered shells with sand mixed in can be considered as a target.On the other hand, even if the concentration of carbon dioxide gas is low, the produced CaCO3 can be converted to high-grade one.
Up to the reaction in Equation (2), carbon dioxide gas from a low Fl place, or even the atmosphere in extreme cases, can be used, and the carbon dioxide in Equation (1) can be self-sufficient, so each component can be is well balanced and there is no waste, and if there is a limestone quarry near the desalination plant, even if only low-grade limestone can be mined, it can be used effectively, which is particularly effective.

【図面の簡単な説明】[Brief explanation of drawings]

図は本発明の一実施例における一部を拡大して示したフ
ローシー1〜である。 (1)・・・・・・淡水化装置、 (2)・・・・・・外部加熱石灰石分解炉、(2′)・
・・加熱分解塔、 (3)・・・・・・蒸 発 器、 (5)・・・・・・カルシウム溶解装置、(6)・・・
・・・ 小ツバ−、 (7)・・・・・・装入用ダブル弁、 (9)・・・・・・加 熱 器、 (12)・・・・・・ブ ロ ア、 (13)・・・・・・冷 却 器、 (14)・・・・・・排 出 弁、 (16)・・・・・・生石灰消化器、 (18)・・・・・・シックナー、
The figure is a partially enlarged flowchart 1 in an embodiment of the present invention. (1)... Desalination equipment, (2)... External heating limestone decomposition furnace, (2')...
... thermal decomposition tower, (3) ... evaporator, (5) ... calcium dissolution device, (6) ...
... Small collar, (7) ... Double valve for charging, (9) ... Heater, (12) ... Blower, (13) )...Cooler, (14)...Discharge valve, (16)...Quicklime digester, (18)...Thickener,

Claims (7)

【特許請求の範囲】[Claims] (1)、淡水化装置の近傍に外部加熱石灰石または苦上
分を含む石灰石(以下石灰石と称する)分解炉を設置し
、生成淡水の一部は石灰石分解炉側に導き、生成生石灰
と混合して石灰乳または消石灰溶液となし、これに石灰
石分解炉燃焼排ガス、一部の石灰石分解ガス、他から得
た炭酸ガスを単独もしくは併用して吸収させ、これと前
記石灰石゛分解炉から発生した高純度炭酸ガスと残りの
生成淡水とを混合吸収させることによって硬度を附与す
ることを特徴とする生成淡水後処理方法。
(1) An externally heated limestone or limestone containing bitter material (hereinafter referred to as limestone) decomposition furnace is installed near the desalination equipment, and a part of the produced fresh water is led to the limestone decomposition furnace and mixed with the produced quicklime. This is made into lime milk or slaked lime solution, and this is made to absorb limestone decomposition furnace combustion exhaust gas, some limestone decomposition gas, and carbon dioxide gas obtained from other sources, either alone or in combination, and this and the limestone generated from the limestone decomposition furnace are combined. A method for post-processing produced fresh water, characterized by imparting hardness by mixing and absorbing pure carbon dioxide gas and remaining produced fresh water.
(2)、淡水化装置の近傍に外部加熱石灰石分解・ 炉
を設置し、生成淡水は石灰石分解炉側に導き、生成生石
灰と混合して消石灰溶液となし、これに石灰石分解炉燃
焼排ガス、一部の石灰石分解ガス、他から得た炭酸ガス
を単独もしくは併用して吸収させ、これに前記石灰石分
解炉から発生した高純度炭酸ガスを混合吸収させること
によって該生成淡水に硬度を附与することを特徴とする
生成淡水後処理方法。
(2) An external heated limestone decomposition/furnace is installed near the desalination equipment, and the produced fresh water is led to the limestone decomposition furnace side and mixed with the produced quicklime to form a slaked lime solution, which is then mixed with the limestone decomposition furnace combustion exhaust gas, Adding hardness to the produced fresh water by absorbing limestone decomposition gas and carbon dioxide gas obtained from other sources, either alone or in combination, and by mixing and absorbing high purity carbon dioxide gas generated from the limestone decomposition furnace. A method for post-treatment of produced fresh water, characterized by:
(3)、淡水化装置と生成淡水が通過するカルシウム溶
解装置が、石灰石ホッパーと装入弁及び排出弁を有する
加熱分解塔と生石灰消化器と第1段炭酸ガス吸収器とを
有する外部加熱石灰石分解炉に近接して設けてなる生成
淡水後処理装置。
(3) The desalination device and the calcium dissolution device through which the produced fresh water passes are externally heated limestone comprising a limestone hopper, a thermal decomposition tower having a charging valve and a discharge valve, a quicklime digester, and a first stage carbon dioxide absorber. A freshwater after-treatment device installed close to the decomposition furnace.
(4)、淡水化装置は蒸発器であり、生成淡水が蒸留水
である特許請求の範囲第3項記載の生成淡水後処理装置
(4) The produced fresh water after-treatment device according to claim 3, wherein the desalination device is an evaporator and the produced fresh water is distilled water.
(5)、淡水化装置は逆浸透圧装置であり、生成淡水が
透過水である特許請求の範囲第3項記載の生成淡水後処
理装置。
(5) The produced fresh water after-treatment device according to claim 3, wherein the desalination device is a reverse osmosis device, and the produced fresh water is permeated water.
(6)、カルシウム溶解装置は基型式または長い配管か
らなる炭酸ガス吸収部分である特許請求の範囲第3項記
載の生成淡水後処理装置。
(6) The produced fresh water after-treatment device according to claim 3, wherein the calcium dissolving device is a basic type or a carbon dioxide absorbing portion consisting of long piping.
(7)、装入弁、排出弁はシール機構を有する特許請求
の範囲第3項、第4項、第5項、第6項記載の生成淡水
後処理装置。
(7) The produced freshwater after-treatment device according to claims 3, 4, 5, and 6, wherein the charging valve and the discharge valve have a sealing mechanism.
JP6480084A 1984-03-30 1984-03-30 Method and apparatus for post-treatment of prepared fresh water Granted JPS60206489A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP6480084A JPS60206489A (en) 1984-03-30 1984-03-30 Method and apparatus for post-treatment of prepared fresh water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP6480084A JPS60206489A (en) 1984-03-30 1984-03-30 Method and apparatus for post-treatment of prepared fresh water

Publications (2)

Publication Number Publication Date
JPS60206489A true JPS60206489A (en) 1985-10-18
JPH0472597B2 JPH0472597B2 (en) 1992-11-18

Family

ID=13268676

Family Applications (1)

Application Number Title Priority Date Filing Date
JP6480084A Granted JPS60206489A (en) 1984-03-30 1984-03-30 Method and apparatus for post-treatment of prepared fresh water

Country Status (1)

Country Link
JP (1) JPS60206489A (en)

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