JPH0472597B2 - - Google Patents
Info
- Publication number
- JPH0472597B2 JPH0472597B2 JP6480084A JP6480084A JPH0472597B2 JP H0472597 B2 JPH0472597 B2 JP H0472597B2 JP 6480084 A JP6480084 A JP 6480084A JP 6480084 A JP6480084 A JP 6480084A JP H0472597 B2 JPH0472597 B2 JP H0472597B2
- Authority
- JP
- Japan
- Prior art keywords
- produced
- limestone
- carbon dioxide
- fresh water
- decomposition furnace
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired
Links
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 claims description 106
- 229910002092 carbon dioxide Inorganic materials 0.000 claims description 53
- 239000001569 carbon dioxide Substances 0.000 claims description 52
- 235000019738 Limestone Nutrition 0.000 claims description 47
- 239000006028 limestone Substances 0.000 claims description 47
- 239000013505 freshwater Substances 0.000 claims description 36
- ODINCKMPIJJUCX-UHFFFAOYSA-N Calcium oxide Chemical compound [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 claims description 26
- 238000000354 decomposition reaction Methods 0.000 claims description 22
- 239000011575 calcium Substances 0.000 claims description 17
- 238000010612 desalination reaction Methods 0.000 claims description 17
- 239000000292 calcium oxide Substances 0.000 claims description 13
- 235000012255 calcium oxide Nutrition 0.000 claims description 13
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 claims description 11
- 229910052791 calcium Inorganic materials 0.000 claims description 11
- 239000000920 calcium hydroxide Substances 0.000 claims description 11
- 235000011116 calcium hydroxide Nutrition 0.000 claims description 11
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical group O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 11
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 claims description 10
- 229910001861 calcium hydroxide Inorganic materials 0.000 claims description 10
- 235000008733 Citrus aurantifolia Nutrition 0.000 claims description 9
- 235000011941 Tilia x europaea Nutrition 0.000 claims description 9
- 239000004571 lime Substances 0.000 claims description 9
- 238000002485 combustion reaction Methods 0.000 claims description 8
- 239000008267 milk Substances 0.000 claims description 7
- 235000013336 milk Nutrition 0.000 claims description 7
- 210000004080 milk Anatomy 0.000 claims description 7
- 238000000034 method Methods 0.000 claims description 6
- 238000005979 thermal decomposition reaction Methods 0.000 claims description 6
- 239000006096 absorbing agent Substances 0.000 claims description 5
- 238000010521 absorption reaction Methods 0.000 claims description 5
- 238000004090 dissolution Methods 0.000 claims description 4
- 238000007789 sealing Methods 0.000 claims description 4
- 239000012153 distilled water Substances 0.000 claims description 2
- 238000001223 reverse osmosis Methods 0.000 claims description 2
- FYYHWMGAXLPEAU-UHFFFAOYSA-N Magnesium Chemical compound [Mg] FYYHWMGAXLPEAU-UHFFFAOYSA-N 0.000 claims 1
- 229910052749 magnesium Inorganic materials 0.000 claims 1
- 239000011777 magnesium Substances 0.000 claims 1
- 238000012805 post-processing Methods 0.000 claims 1
- 239000007789 gas Substances 0.000 description 38
- VTYYLEPIZMXCLO-UHFFFAOYSA-L Calcium carbonate Chemical compound [Ca+2].[O-]C([O-])=O VTYYLEPIZMXCLO-UHFFFAOYSA-L 0.000 description 15
- 238000006243 chemical reaction Methods 0.000 description 10
- 235000010216 calcium carbonate Nutrition 0.000 description 9
- 239000002245 particle Substances 0.000 description 8
- 229910000019 calcium carbonate Inorganic materials 0.000 description 6
- 238000010438 heat treatment Methods 0.000 description 5
- 239000012535 impurity Substances 0.000 description 5
- OAKJQQAXSVQMHS-UHFFFAOYSA-N Hydrazine Chemical compound NN OAKJQQAXSVQMHS-UHFFFAOYSA-N 0.000 description 4
- NKWPZUCBCARRDP-UHFFFAOYSA-L calcium bicarbonate Chemical compound [Ca+2].OC([O-])=O.OC([O-])=O NKWPZUCBCARRDP-UHFFFAOYSA-L 0.000 description 4
- 229910000020 calcium bicarbonate Inorganic materials 0.000 description 4
- BVKZGUZCCUSVTD-UHFFFAOYSA-M Bicarbonate Chemical compound OC([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-M 0.000 description 3
- 239000000446 fuel Substances 0.000 description 3
- 239000013535 sea water Substances 0.000 description 3
- HZAXFHJVJLSVMW-UHFFFAOYSA-N 2-Aminoethan-1-ol Chemical compound NCCO HZAXFHJVJLSVMW-UHFFFAOYSA-N 0.000 description 2
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 2
- CPLXHLVBOLITMK-UHFFFAOYSA-N Magnesium oxide Chemical compound [Mg]=O CPLXHLVBOLITMK-UHFFFAOYSA-N 0.000 description 2
- 239000000919 ceramic Substances 0.000 description 2
- 239000010459 dolomite Substances 0.000 description 2
- 229910000514 dolomite Inorganic materials 0.000 description 2
- 239000003651 drinking water Substances 0.000 description 2
- 235000020188 drinking water Nutrition 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 239000002002 slurry Substances 0.000 description 2
- 229910018072 Al 2 O 3 Inorganic materials 0.000 description 1
- WKBOTKDWSSQWDR-UHFFFAOYSA-N Bromine atom Chemical compound [Br] WKBOTKDWSSQWDR-UHFFFAOYSA-N 0.000 description 1
- 239000002196 Pyroceram Substances 0.000 description 1
- 241001653678 Russula emetica Species 0.000 description 1
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical group [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 1
- 229910021529 ammonia Inorganic materials 0.000 description 1
- GDTBXPJZTBHREO-UHFFFAOYSA-N bromine Substances BrBr GDTBXPJZTBHREO-UHFFFAOYSA-N 0.000 description 1
- 229910052794 bromium Inorganic materials 0.000 description 1
- 239000011195 cermet Substances 0.000 description 1
- 239000003795 chemical substances by application Substances 0.000 description 1
- 238000001816 cooling Methods 0.000 description 1
- 238000007599 discharging Methods 0.000 description 1
- 230000035622 drinking Effects 0.000 description 1
- 230000005611 electricity Effects 0.000 description 1
- 238000001704 evaporation Methods 0.000 description 1
- 230000008020 evaporation Effects 0.000 description 1
- 239000010419 fine particle Substances 0.000 description 1
- 230000005802 health problem Effects 0.000 description 1
- 239000003779 heat-resistant material Substances 0.000 description 1
- 229910001026 inconel Inorganic materials 0.000 description 1
- 229910052500 inorganic mineral Inorganic materials 0.000 description 1
- 238000009434 installation Methods 0.000 description 1
- 239000000395 magnesium oxide Substances 0.000 description 1
- 239000012528 membrane Substances 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 235000010755 mineral Nutrition 0.000 description 1
- 239000011707 mineral Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000003208 petroleum Substances 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 239000012264 purified product Substances 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 230000035484 reaction time Effects 0.000 description 1
- 230000009257 reactivity Effects 0.000 description 1
- 239000004576 sand Substances 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
- 239000002904 solvent Substances 0.000 description 1
- 229910052717 sulfur Inorganic materials 0.000 description 1
- 239000011593 sulfur Substances 0.000 description 1
- 238000010408 sweeping Methods 0.000 description 1
- 239000008399 tap water Substances 0.000 description 1
- 235000020679 tap water Nutrition 0.000 description 1
- 239000002562 thickening agent Substances 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
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
道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 by a desalination device into water quality suitable for tap water. .
石灰石の石灰の一部が苦土で入れ替つた白雲石
(ドロマイト)系を含んでも全く同軌の反応とな
るので、本発明では一々の説明は省略するが、
Caで示される部分はすべてCa+Mgである場合
を含むものとする。 Even if dolomite (dolomite), in which some of the lime in limestone is replaced by magnesia, the reaction is exactly the same, so a detailed explanation will be omitted in the present invention.
All portions indicated by Ca include cases where Ca+Mg is present.
淡水化装置によつ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
乏しいものであつた。これらの欠点は補うため、
淡水に炭酸カルシウムや消石灰や炭酸ガスとを添
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
ンフイルターが配置され、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。 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. To compensate for these shortcomings,
The method used is to add calcium carbonate, slaked lime, and carbon dioxide gas to fresh water to make manufactured water.Generally, a container filled with limestone, a so-called limestone filter, is placed, and the fresh water that has absorbed carbon dioxide gas is passed through it. After passing through, calcium hydrogen carbonate is produced by the following reaction and hardness increases.
CaCO3+H2O+CO2→Ca(HCO3)2 ……(1)
このライムストンフイ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イルターは
容量の割に淡水の処理量は低く、よつて大型塩水
淡水化装置では該フイ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
イルターに投入しなければならず、この補充作業
は付溶解スライムの排出作業とともに仲々煩雑で
あつた。 CaCO 3 + H 2 O + CO 2 → Ca (HCO 3 ) 2 ...(1) This limestone filter is usually filled with readily available and inexpensive limestone with a particle size of 2 to 20 mm, but in many cases the purity is low and contains impurities,
In addition, the dissolution rate is slow, and even if hardness is imparted, the quality of the water may be poor, and the amount of freshwater that can be processed by this limestone filter is low relative to its capacity. As a result, equipment costs were high, and limestone had to be added to each filter, and this replenishment work, along with the work of discharging the dissolved slime, was quite complicated.
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
合、抽気抽の炭酸ガスにはヒドラジン等が混入す
る恐れがあり問題である。 On the other hand, carbon dioxide gas can sometimes be obtained by decomposing and extracting bicarbonate components in seawater in desalination equipment, so it is reasonable to use this gas, but in this case, it may contain impurities such as ammonia, oil, and bromine. This is dangerous, and if hydrazine is used as a deoxidizing agent for the boiler of the steam for the bleed ejector, there is a risk that hydrazine or the like will be mixed into the extracted carbon dioxide gas, 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
複雑となつ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はない。即ち
この場合の数+Nm3/H(CO2として)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 the process of recovering carbon dioxide gas produced by burning oil or gas using a solvent such as ethanolamine;
Alternatively, it is possible to use purchased liquefied carbon dioxide, but in the former case, the equipment would be of the same type as a large-scale device, which would not only be complicated and require more power for pumps, etc., but also require a large number of equipment and be expensive to construct. Therefore, health problems remain. The latter is not practical as it would lead to a rise in price (running costs). That is, in this case, the former is an unreasonable scale-down for the requirement of about 3000 ml + Nm 3 /H (as CO 2 ), and the latter requires a little too much consumption and is accompanied by concerns about running out of supply.
上気のとおり炭酸ガスの必要量な数+Nm3/H
(CO2として)の能力であり、石灰石としても100
Kg/H程度の微々たる取扱数量となり、此の量に
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+mmφ以上の石灰石に比して分
解時間も桁違いに短く、従つて滞留量も僅かなも
のとなり、後記セラミツク管などの管内で加熱す
るに適する程度となるほど、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
つても、より高純度に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炭酸ガスを利用し
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カルシウ
ム微粒の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→CaCO3+H2O ……(2)
の反応によつて稀薄な炭酸ガスをも捉えて炭酸カ
ルシウムを生成させ、該生成炭酸カルシウムに更
に淡水の炭酸ガスを(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つて、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と取得を目的として
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 per the above air, the required amount of carbon dioxide + Nm 3 /H
(as CO2 ) and as limestone 100
The amount handled is very small, about Kg/H, and the small diameter limestone corresponding to this amount is continuously processed, and the decomposition time is orders of magnitude shorter than that for industrial-scale limestone larger than number + mmφ. The amount of stagnation is also small, and the concept is completely different from that of conventional limestone furnaces, as it is suitable for heating inside pipes such as ceramic pipes, which will be described later.The present invention is based on a newly developed ultra-small limestone decomposition furnace. organically combined with a desalination device to produce a higher purity slaked lime solution or lime milk even in the case of slightly lower grade limestone, and then using lower purity carbon dioxide gas to first produce a higher purity slaked lime solution or lime milk. A slurry of calcium carbonate particles is produced, and the calcium carbonate particles are reacted with generated carbon dioxide gas 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 → CaCO 3 + H 2 O ...(2) captures even dilute carbon dioxide gas to generate calcium carbonate. This is a method of dissolving calcium bicarbonate in fresh water by reacting calcium carbonate with carbon dioxide gas in fresh water using the formula (1), and is economical, allows for miniaturization and continuous use of equipment, and is stable enough to pass water quality standards. This was done for the purpose of obtaining 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TDSを数ppmしか含まず、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附与する。 An external heating limestone decomposition furnace 2 is installed close to the installation location of a desalination device, for example, a seawater desalination evaporation device 1, and the distilled water, which is fresh water produced from the evaporator 3, contains only a few ppm of TDS. Since it is not suitable for drinking as it is, in order to reform it, pipe 4
After that, it is introduced into a calcium dissolving device 5 whose details will be described later, and hardness is imparted as described later.
一方、拡大して示された石灰石分解炉2は外部
加熱方式であつて、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+mmと超小形の
管を使用することができ、上部のホツパー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
つて炉壁10を介して900℃以上に加熱され、生
石灰の炭酸ガスに分解し、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によつ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とも有利な方法と
考えられる。装入弁7及び排出弁14ちなそれぞ
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えの洩れを防ぐた
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、後の工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、セラミツクスとしては例えばSiC、
Al2O3、その他パイロセラム、サーメツト等の耐
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. A tube as small as +mm can be used, and the limestone 8, which is about several mm in size, is charged into the furnace from the upper hopper 6 through the charging double valve 7, and is It is heated to 900°C or more through the furnace wall 10 by a heater 9 such as a burner using petroleum as fuel, decomposing quicklime into carbon dioxide gas, and while the quicklime passes through the cooling zone 11 at the bottom of the furnace, After being indirectly cooled by a cooler 13 through which air from 12 flows, it falls through a pipe 15 with a discharge valve 14 into a quicklime digester 16 in the lower part. 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 are each provided with a sealing mechanism (not shown) to prevent air from entering, and the pipe 15 is filled with a sealing gas to prevent the generated carbon dioxide from leaking to the outside. Of course, other means may be taken, but it is particularly preferable to use water vapor, which will condense in a later step, for sealing or sweeping without lowering the purity of the carbon dioxide gas. The material for the furnace wall is heat-resistant metal such as Inconel, and ceramics such as SiC,
Use Al 2 O 3 and other heat-resistant materials such as pyroceram and cermet.
生石灰消化器16には淡水化装置1とカルシウ
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ツクナー18により不
純物は沈泥となつて下部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。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2
4を通過する燃焼用空気の熱交換して冷却された
のち、管25によつて底部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CaCO3を生成する。このCaCO3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
される。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。 The fresh water before entering the desalination device 1 and calcium dissolving device 5 is charged into the quicklime digester 16 via a branch pipe 17, and a slaked lime solution or lime milk is produced in the device, and is then processed by a thickener 18 provided inside. Impurities become silt and are discharged from the lower part 19, and purified products are sent to the first stage carbon dioxide absorber 21 through a pipe 20. In the quicklime digester 16, when the purity of the charged quicklime is high, a long pipe can be used instead of a container. First stage carbon dioxide absorption tower 21
The 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 2 in the heat exchanger 23.
After being cooled by heat exchange with the combustion air passing through 4, it is ejected to the bottom 26 through a pipe 25, and the carbon dioxide in the exhaust gas reacts with the slaked lime solution or milk of lime in the vessel to produce CaCO 3 . do. This CaCO 3 has a small particle size and is convenient for subsequent transport and reaction. Excess exhaust gas is discharged to the atmosphere through the upper pipe 27. In this way, low-purity carbon dioxide gas can be used for CaCO 3 production, 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る。こ
こで生成したCaCO3は粒径が小さいからスラリ
ー状となつてポンプ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に到つてここを通過する淡水に混合す
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
化装置の排気ガス、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併せて利用してもよ
い。 Note that a circulating water guide cylinder 28 is provided inside the first stage carbon dioxide absorber 21 to allow the reaction to occur smoothly. Since the CaCO 3 generated here has a small particle size, it becomes a slurry and flows through the pump 29 and the pipe 30.
CaCO 3 reaches the calcium dissolving device 5 at a concentration of, for example, about 0.5% and is mixed with the fresh water passing therethrough. In addition to the above-mentioned combustion exhaust gas, the first stage carbon dioxide absorber 21 also contains some limestone decomposition gas, carbon dioxide obtained from other sources, such as boiler exhaust gas, seawater desalination equipment exhaust gas, or purity levels in the air. Low carbon dioxide gas 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、場合によつては管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1
6を用いず長い配管で代用することもできる。 In the above description, a portion of the produced fresh water is introduced into the quicklime digester 16, but in some cases, the pipe 4 may be omitted and the entire amount of produced fresh water may be introduced. In this case, if the limestone is of good purity and has almost no impurities, container 1
It is also possible to use a long pipe instead of 6.
石灰石分解炉2の加熱分解塔2′内部で石灰石
の分解によつて生じた炭酸ガスは高純度を保ち、
管31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、H2O、CO2が
反応してCa(HCO3)が溶解生成し、淡水に硬度
を附与する。この際、CaCO3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
ストンフイルターのような大規模な装置を必要と
しない。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+ppm程度で
あるから、管30を流れる0.5%程度のCaCO3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つて、そ
の反応時間は短かくなり、カルシウム溶解装置5
は小形にでき、内部機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
塔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 carbon dioxide gas generated by the decomposition of limestone inside the thermal decomposition tower 2' of the limestone decomposition furnace 2 maintains high purity.
Calcium enters the dissolving device 5 through the pipe 31 and is dissolved in fresh water, and CaCO 3 , H 2 O, and CO 2 react in the dissolving device 5 to dissolve and generate Ca (HCO 3 ), which imparts hardness to the fresh water. do. At this time, since CaCO 3 has a small particle size as described above, the reaction rate is high, and a large-scale device such as a conventional limestone filter is not required. The hardness required for the fresh water taken out from the pipe 32 after treatment is approximately several ppm in terms of hydrogen carbonate ions, so the production of this level of hydrogen carbonate ions from the approximately 0.5% CaCO 3 flowing through the pipe 30 is limited to the amount of carbon dioxide gas used. Coupled with the high purity and ease of dissolution, the reaction time is short and the calcium dissolution device 5
It can be made small and the internal mechanism is extremely simple.In short, it only needs to be able to mix and dissolve sufficiently, and the carbon dioxide absorption part that carries out the reaction with a simple tower type or piping as shown in the figure with an appropriate length can be used. 33 is sufficient.
生成成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
ではない。 When some of the produced lime can be used for purposes other than the main post-treatment in the vicinity, a portion of the high-purity carbon dioxide generated by heating the limestone can be used instead of the low-purity carbon dioxide. Although it can be used, the amount of heat required to heat the limestone to produce the carbon dioxide gas in this area consumes 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か
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イ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
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つて、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)2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等となつ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 from 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 discarded. 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. When the amount of carbon dioxide from the decomposition furnace alone is insufficient due to the furnace conditions or the type of fuel used in the heater 9, the permeated water may absorb carbon dioxide depending on the type of membrane, such as during desalination by reverse osmosis. When there is not much carbon dioxide in the air, or when there is no carbon dioxide source such as combustion exhaust gas or bleed gas nearby, several hundred ppm of carbon dioxide in the air can be captured by installing an absorption tower due to the strong reactivity of Ca(OH) 2 . You can also fill in the gaps by doing so. Furthermore, if there is sulfur in the fuel, the amount captured as CaSO 4 etc. can also be an effective source of calcium.
しかも、この炭酸ガスの添加によつて粒径の小
さいCaCO3が生成するので以後のカルシウム溶
解装置における溶け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
ムストンフイ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
で該溶解装置は小形で形状は単純化でき、淡水の
通過速度は大となし得て処理能力が増大し、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
のところまでは低濃度の炭酸ガス、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、淡水の後処理において各成分はバ
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
石灰石した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。 Moreover, since CaCO 3 having a small particle size is generated by adding carbon dioxide gas, the reaction rate with easily soluble high purity carbon dioxide gas 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, which is about several millimeters in size, the dissolving device can be small and simple in shape, and the passing speed of fresh water can be increased. This has the effect of increasing the processing capacity, and if there is some leeway in the pipe length, it can be made smaller by using a part of it, or new additional equipment can be omitted, and it also has the effect of reducing the amount of limestone with inferior purity. It is also possible to operate using small particles as raw material.
Weathered shells mixed with sand are also considered as targets.
On the other hand, even if the concentration of carbon dioxide gas is low,
CaCO 3 can be converted into a high-grade product, and low-concentration carbon dioxide gas, or even the atmosphere in extreme cases, can be used for the reaction in equation (2), and the carbon dioxide in equation (1) can be self-sufficient. In the post-treatment of freshwater, each component is well balanced and there is no waste, and if there is a limestone quarry near the desalination equipment, even if low-grade limestone cannot be mined, it can be used effectively. is large.
図は本発明の一実施例における一部を拡大して
示したフローシートである。
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……ホツパー、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……シツクナー、21……第1段
炭酸ガス吸収器、33……CO2吸収部分。
The figure is a flow sheet showing an enlarged part of one embodiment of the present invention. 1... Desalination equipment, 2... External heating limestone decomposition furnace, 2'... Thermal decomposition tower, 3... Evaporator, 5...
Calcium dissolving device, 6...hopper, 7...double valve for charging, 9...heater, 12...blower,
13...Cooler, 14...Discharge valve, 16...Quicklime digester, 18...Sickener, 21...First stage carbon dioxide absorber, 33...CO 2 absorption part.
Claims (1)
土分を含む石灰石(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つて硬度を附与する
ことを特徴とする生成淡水後処理方法。 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つて該生成淡
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。 3 淡水化装置で製造された生成淡水の一部を生
石灰消化器に配管等により導き石灰乳又は消石灰
溶液とした後、当該石灰乳又は消石灰溶液を配管
等により第1段炭酸ガス吸収器へ導き、前記加熱
分解塔で生じた燃焼排ガス中の炭酸ガスと反応さ
せた後配管等で、更に別途前記加熱分解塔で石灰
石等の加熱分解により発生した炭酸ガスを配管等
でカルシウム溶解装置に導き前記生成淡水の残部
と共に混合、溶解する構成より成る生成淡水後処
理装置。 4 淡水化装置は蒸発器であり、生成淡水が蒸溜
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 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。 6 カルシウム溶解装置は塔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。 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。[Claims] 1. An externally heated limestone or limestone containing magnesium (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 the produced quicklime is This is mixed with lime milk or slaked lime solution, and this is used to absorb limestone decomposition furnace combustion exhaust gas, some limestone decomposition gas, and carbon dioxide gas obtained from other sources, alone or in combination, and this and the limestone decomposition furnace generates. A method for post-processing produced fresh water, characterized in that hardness is imparted by mixing and absorbing high-purity carbon dioxide gas and remaining produced fresh water. 2. An externally heated limestone decomposition furnace is installed near the desalination equipment, and the produced fresh water is guided to the limestone decomposition furnace side and mixed with the produced quicklime to form a slaked lime solution. It is characterized by imparting hardness to the produced fresh water by absorbing gas or carbon dioxide obtained from other sources alone or in combination, and mixing and absorbing high-purity carbon dioxide generated from the limestone decomposition furnace. A method for post-treatment of produced fresh water. 3. A part of the fresh water produced by the desalination equipment is led to a quicklime digester through piping, etc. to make lime milk or slaked lime solution, and then the lime milk or slaked lime solution is led to the first stage carbon dioxide absorber through piping, etc. After reacting with carbon dioxide in the combustion exhaust gas generated in the thermal decomposition tower, carbon dioxide gas generated by thermal decomposition of limestone, etc. in the thermal decomposition tower is further led to the calcium dissolving device through a piping, etc. A produced freshwater after-treatment device configured to mix and dissolve produced freshwater with the remainder of the produced freshwater. 4. The produced fresh water post-treatment device according to claim 3, wherein the desalination device is an evaporator and the produced fresh water is distilled water. 5. The produced fresh water post-treatment device according to claim 3, wherein the desalination device is a reverse osmosis device, and the produced fresh water is permeated water. 6. The produced freshwater after-treatment device according to claim 3, wherein the calcium dissolution device is a carbon dioxide absorption section consisting of a tower type or long piping. 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.
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 JPS60206489A (en) | 1985-10-18 |
| JPH0472597B2 true 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) |
Families Citing this family (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| PL2623466T3 (en) * | 2012-02-03 | 2017-09-29 | Omya International Ag | Process for the preparation of an aqueous solution comprising at least one earth alkali hydrogen carbonate and its use |
| EP2623467B1 (en) * | 2012-02-03 | 2016-04-27 | Omya International AG | Process for the preparation of an aqueous solution comprising at least one earth alkali hydrogen carbonate and its use |
| IT202000031562A1 (en) * | 2020-12-22 | 2022-06-22 | Giovanni Cappello | PLANT AND METHOD FOR THE PRODUCTION OF DECARBONIZED OXIDE OR HYDROXIDE USING CARBONATE AND ELECTRIC ENERGY |
| IT202200016347A1 (en) * | 2022-08-01 | 2024-02-01 | Limenet Srl Soc Benefit | SYSTEM AND METHOD TO IMPROVE THE EFFICIENCY OF CO2 CAPTURE AND STORAGE USING PRECIPITATED CALCIUM CARBONATE |
-
1984
- 1984-03-30 JP JP6480084A patent/JPS60206489A/en active Granted
Also Published As
| Publication number | Publication date |
|---|---|
| JPS60206489A (en) | 1985-10-18 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN101797466B (en) | Wet flue gas desulphurizing method utilizing carbide slag slurry and device thereof | |
| JP5345954B2 (en) | Carbon dioxide sequestration process, a system for sequestering carbon dioxide from a gas stream | |
| CN104707454B (en) | Tower flue gases of cock oven UTILIZATION OF VESIDUAL HEAT IN and simultaneous SO_2 and NO removal system | |
| CN102773006A (en) | Device and process for cyclic capture of carbon dioxide by taking CaO as carrier | |
| US20100196244A1 (en) | Method and device for binding gaseous co2 to sea water for the flue gas treatment with sodium carbonate compounds | |
| CN102395417A (en) | Systems, devices and methods for sequestering carbon dioxide | |
| WO2019225202A1 (en) | Treatment method for reducing carbon dioxide discharge amount of combustion exhaust gas | |
| CN103974757A (en) | Method and system for capturing carbon dioxide from a gas stream | |
| US10239762B2 (en) | Power plant for producing energy and ammonia | |
| US12070720B2 (en) | Plant and method for producing decarbonized oxide or hydroxide using carbonate and electric power | |
| CN104817102B (en) | A system device and process for liquid-phase indirect capture of carbon dioxide in mineralized flue gas | |
| US10351456B2 (en) | Process for treatment of sour water generated from coal gasification | |
| CN101890283A (en) | Production process for removing carbon dioxide from smoke and preparing ammonium compound fertilizer and light calcium carbonate | |
| JP7377639B2 (en) | Mercury recovery equipment and mercury recovery method | |
| CN202427348U (en) | System for removing carbon dioxide in smoke and preparing ammonium sulfate compound fertilizer and light calcium carbonate | |
| JPH0472597B2 (en) | ||
| JP2001354975A (en) | Coal gasification and ash melting furnace and combined cycle system | |
| CN111672879B (en) | A waste salt resource utilization system and method based on integrated energy conservation and environmental protection of thermal power plants | |
| CN101641145B (en) | System, apparatus and method for carbon dioxide sequestration | |
| CN103611401B (en) | A kind of bittern purifying waste residue sulfur removal technology | |
| CN208604069U (en) | A kind of useless organic matter comprehensive utilization processing system | |
| JPH0450879B2 (en) | ||
| CN101642667B (en) | Method for using cooling-tower circulating water as water used by flue gas desulfurization system | |
| US4255388A (en) | Apparatus for the production of H2 S from SO2 obtained from flue gas | |
| CN114471107A (en) | A kind of double alkali decarburization process and equipment |