TWI485003B - Method for producing tetraalkylammonium salt solution - Google Patents
Method for producing tetraalkylammonium salt solution Download PDFInfo
- Publication number
- TWI485003B TWI485003B TW100127414A TW100127414A TWI485003B TW I485003 B TWI485003 B TW I485003B TW 100127414 A TW100127414 A TW 100127414A TW 100127414 A TW100127414 A TW 100127414A TW I485003 B TWI485003 B TW I485003B
- Authority
- TW
- Taiwan
- Prior art keywords
- packed column
- taa
- aqueous solution
- packed
- production line
- Prior art date
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C07—ORGANIC CHEMISTRY
- C07C—ACYCLIC OR CARBOCYCLIC COMPOUNDS
- C07C209/00—Preparation of compounds containing amino groups bound to a carbon skeleton
- C07C209/82—Purification; Separation; Stabilisation; Use of additives
- C07C209/84—Purification
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D15/00—Separating processes involving the treatment of liquids with solid sorbents; Apparatus therefor
- B01D15/08—Selective adsorption, e.g. chromatography
- B01D15/26—Selective adsorption, e.g. chromatography characterised by the separation mechanism
- B01D15/36—Selective adsorption, e.g. chromatography characterised by the separation mechanism involving ionic interaction
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J39/00—Cation exchange; Use of material as cation exchangers; Treatment of material for improving the cation exchange properties
- B01J39/04—Processes using organic exchangers
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/42—Treatment of water, waste water, or sewage by ion-exchange
-
- C—CHEMISTRY; METALLURGY
- C07—ORGANIC CHEMISTRY
- C07C—ACYCLIC OR CARBOCYCLIC COMPOUNDS
- C07C211/00—Compounds containing amino groups bound to a carbon skeleton
- C07C211/62—Quaternary ammonium compounds
- C07C211/63—Quaternary ammonium compounds having quaternised nitrogen atoms bound to acyclic carbon atoms
Landscapes
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Analytical Chemistry (AREA)
- Treatment Of Water By Ion Exchange (AREA)
- Photosensitive Polymer And Photoresist Processing (AREA)
- Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)
Description
本發明係有關於使用陽離子交換樹脂的四烷基銨鹽水溶液的新的製造方法。詳細地說,是有關於如下的四烷基銨(以下,將四烷基銨簡稱為TAA)鹽水溶液的製造方法:向填充有陽離子交換樹脂的填充塔中通入含有氫氧化TAA的顯影廢液,使TAA離子吸附於陽離子交換樹脂,接著使陽離子交換樹脂與酸接觸,使被陽離子交換樹脂吸附的TAA離子溶離,獲得高濃度的TAA鹽水溶液,此時,可防止TAA離子在向陽離子交換樹脂吸附時從填充塔洩漏,並有效地使TAA離子吸附於填充塔中的陽離子交換樹脂。The present invention relates to a novel process for the production of an aqueous solution of a tetraalkylammonium salt using a cation exchange resin. Specifically, it is a method for producing a tetraalkylammonium (hereinafter, a tetraalkylammonium abbreviated as TAA) salt aqueous solution: a developing waste containing TAA hydroxide is introduced into a packed column packed with a cation exchange resin. The liquid is caused to adsorb TAA ions to the cation exchange resin, and then the cation exchange resin is contacted with the acid to dissolve the TAA ions adsorbed by the cation exchange resin to obtain a high concentration of the TAA salt aqueous solution. At this time, the TAA ions are prevented from being exchanged for the cations. The resin leaks from the packed column during adsorption and effectively adsorbs TAA ions to the cation exchange resin in the packed column.
在半導體和液晶製造工程中進行如下的顯影工程:在晶圓、玻璃等基板上形成圖案時,在形成於基板表面的金屬層上塗布由酚醛樹脂、聚苯乙烯樹脂等構成的負型(negative type)或正型(positive type)的抗蝕劑,介隔著用於形成該圖案的光罩對其進行曝光,使用以氫氧化TAA物為主要成分的顯影液對未硬化部分或硬化部分進行顯影,然後進行蝕刻,從而在上述金屬層上形成圖案。在該工程中,排出含有氫氧化TAA的顯影工程廢液。In a semiconductor and liquid crystal manufacturing process, a development process is performed in which a pattern formed on a substrate such as a wafer or a glass is coated with a negative type composed of a phenol resin, a polystyrene resin, or the like on a metal layer formed on the surface of the substrate (negative Type) or a positive type resist, which is exposed by a photomask for forming the pattern, and the unhardened portion or the hardened portion is performed using a developer containing TAA as a main component Development is then performed by etching to form a pattern on the above metal layer. In this project, the development engineering waste liquid containing TAA hydroxide is discharged.
另外,在利用顯影液進行顯影後,為了除去殘留在基板上的顯影液而利用超純水進行洗滌,在該洗滌工程後,排出含有氫氧化TAA的洗滌工程廢液。這些顯影廢液和洗滌工程廢液通常在各自混合後作為含有氫氧化TAA的顯影廢液被排放。近年來,隨著半導體和液晶的生產量增大,上述顯影液的消耗量增加,含有氫氧化TAA的顯影廢液的排放量也增加。最近,提出了從該含有氫氧化TAA的顯影廢液中將氫氧化TAA回收、純化而再利用的氫氧化TAA的回收方法。Further, after development by the developer, in order to remove the developer remaining on the substrate, it is washed with ultrapure water, and after the washing process, the washing waste liquid containing TAA of hydroxide is discharged. These developing waste liquids and washing engineering waste liquids are usually discharged as development waste liquid containing TAA after each being mixed. In recent years, as the production amount of semiconductors and liquid crystals has increased, the consumption of the developer has increased, and the amount of development waste liquid containing TAA has also increased. Recently, a method for recovering TAA from which TAA is recovered and purified from the developing waste liquid containing TAA is proposed.
將上述顯影工程廢液和洗滌工程廢液混合而排放的含有氫氧化TAA的顯影廢液中的氫氧化TAA濃度通常為100~10,000ppm左右的低濃度。The TAA concentration in the developing waste liquid containing TAA discharged by mixing the development engineering waste liquid and the washing engineering waste liquid is usually a low concentration of about 100 to 10,000 ppm.
因此,為了效率良好地從含有氫氧化TAA的顯影廢液中將氫氧化TAA回收、純化而獲得高濃度的氫氧化TAA的溶液,提高上述廢液中的氫氧化TAA濃度的濃縮手段是必不可少的。Therefore, in order to efficiently recover and purify the TAA from the developing waste liquid containing TAA, a solution of a high concentration of TAA hydroxide is obtained, and a concentration means for increasing the concentration of the hydroxide TAA in the waste liquid is indispensable. Less.
作為上述濃縮手段,例如,提案了如下方法:使顯影廢液中的氫氧化TAA與陽離子交換樹脂等陽離子交換體接觸,使TAA離子吸附於陽離子交換體,接著使酸水溶液與陽離子交換體接觸,使TAA離子從該樹脂溶離,從而獲得TAA鹽水溶液(參照專利文獻1)。As the above-mentioned concentration means, for example, a method is proposed in which a TAA of a developing waste liquid is brought into contact with a cation exchanger such as a cation exchange resin, and TAA ions are adsorbed to the cation exchanger, and then the aqueous acid solution is brought into contact with the cation exchanger. TAA ions are eluted from the resin to obtain a TAA salt aqueous solution (see Patent Document 1).
或者是,還提案了如下方法:使含有氫氧化TAA的光致抗蝕劑廢液串聯地流過填充有離子交換樹脂的多個吸附槽,使TAA離子吸附於該樹脂,然後使再生液並聯地流過前述多個吸附槽,將前述TAA離子從前述離子交換樹脂溶離(參照專利文獻2)。Alternatively, a method is also proposed in which a photoresist waste liquid containing TAA hydroxide is passed through a plurality of adsorption tanks filled with an ion exchange resin in series, TAA ions are adsorbed to the resin, and then the regeneration liquid is connected in parallel. The TAA ions are eluted from the ion exchange resin by flowing through the plurality of adsorption grooves (see Patent Document 2).
上述專利文獻1和2中記載的方法利用了TAA鹽在水中的溶解度高於氫氧化TAA這一情況。亦即,利用酸進行的TAA離子的溶離可以以少於與陽離子交換樹脂接觸的上述顯影廢液的量進行,因而,結果可以獲得含有比顯影廢液濃度高的TAA離子的TAA鹽水溶液。The methods described in the above Patent Documents 1 and 2 utilize the case where the solubility of the TAA salt in water is higher than that of the hydroxide TAA. That is, the elution of the TAA ions by the acid can be carried out in an amount less than the above-mentioned developing waste liquid which is in contact with the cation exchange resin, and as a result, a TAA salt aqueous solution containing TAA ions having a higher concentration than the developing waste liquid can be obtained.
而且,所得TAA鹽水溶液可通過電解等轉換成氫氧化TAA的水溶液。Further, the obtained TAA salt aqueous solution can be converted into an aqueous solution of TAA hydroxide by electrolysis or the like.
專利文獻1:日本特開平6-142649號公報Patent Document 1: Japanese Patent Laid-Open No. Hei 6-142649
專利文獻2:日本特開2004-066102公報Patent Document 2: Japanese Patent Laid-Open Publication No. 2004-066102
然而,本發明人等對上述專利文獻1中記載的方法進行了驗證試驗,結果判明:相對於填充在填充塔中的陽離子交換樹脂的總交換容量,未進行充分的TAA離子的吸附,在有效地從含有氫氧化TAA的顯影廢液中回收TAA離子的方面存在著問題。However, the inventors of the present invention conducted a verification test on the method described in Patent Document 1, and as a result, it was found that sufficient adsorption of TAA ions was not performed with respect to the total exchange capacity of the cation exchange resin filled in the packed column, and it was effective. There is a problem in the recovery of TAA ions from the developing waste liquid containing TAA hydroxide.
亦即,向填充有陽離子交換樹脂的填充塔中通入含有氫氧化TAA的顯影廢液,追蹤從該填充塔排出的排出液中的TAA離子隨時間的變化,結果,從所填充的陽離子交換樹脂的總交換容量的約一半被交換成TAA離子時起,開始在排出液中檢出TAA離子,發生了TAA離子到排出液中的洩漏。That is, a developing waste liquid containing TAA hydroxide is introduced into a packed column packed with a cation exchange resin, and changes in TAA ions in the discharged liquid discharged from the packed column are tracked with time, and as a result, exchanged cations are exchanged. When about half of the total exchange capacity of the resin is exchanged for TAA ions, TAA ions are detected in the discharge liquid, and leakage of TAA ions into the discharge liquid occurs.
進而判明:繼續通入含有氫氧化TAA的顯影廢液時,所通入的顯影廢液中的一部分TAA離子被填充塔中的陽離子交換樹脂所吸附,但洩漏到排出液中的TAA離子量也增加,隨著陽離子交換樹脂的交換率(所吸附的TAA離子的量相對於陽離子交換樹脂的總交換容量的比例)增加,所通入的顯影廢液中的TAA離子的吸附率(亦即,被吸附的TAA離子的量相對於所通入的顯影廢液中的總TAA離子量的比例)大幅降低。Further, it was found that when the developing waste liquid containing TAA was continuously supplied, a part of the TAA ions in the developed developing waste liquid were adsorbed by the cation exchange resin in the packed column, but the amount of TAA ions leaking into the discharged liquid was also Increasing, as the exchange rate of the cation exchange resin (the ratio of the amount of the adsorbed TAA ions to the total exchange capacity of the cation exchange resin) increases, the adsorption rate of the TAA ions in the developed waste liquid (ie, The ratio of the amount of adsorbed TAA ions to the amount of total TAA ions in the developed developing waste liquid is greatly reduced.
正如由以上驗證試驗也可看出那般,雖然透過在TAA離子洩漏到從填充塔排出的排出液時停止供給含有TAA離子的顯影廢液並通入酸水溶液的方式,可以不損失該顯影廢液中的TAA離子地進行TAA鹽水溶液的回收,但是通過一次吸附處理能夠回收的TAA鹽水溶液的量會變少。As can be seen from the above verification test, although the development waste liquid containing TAA ions is stopped and the acid aqueous solution is supplied when the TAA ions leak to the discharge liquid discharged from the packed column, the development waste can be omitted. The TAA salt solution is recovered from the TAA ion in the liquid, but the amount of the TAA salt aqueous solution that can be recovered by one adsorption treatment is reduced.
或者是,繼續通入含有氫氧化TAA的顯影廢液,直至TAA離子的吸附量達到所填充的陽離子交換樹脂的總交換容量的80~90%左右,在該情況下,通過一次吸附處理能夠回收的TAA鹽水溶液的量會變多,但同時洩漏到排出液中的TAA離子的量也會增加,從所通入的含有氫氧化TAA的顯影廢液中回收TAA離子的回收率會大幅降低。Alternatively, the developing waste liquid containing TAA may be continuously passed until the adsorption amount of the TAA ions reaches about 80 to 90% of the total exchange capacity of the filled cation exchange resin. In this case, it can be recovered by one adsorption treatment. The amount of the TAA brine solution is increased, but the amount of TAA ions leaking into the discharge liquid is also increased, and the recovery rate of recovering TAA ions from the developed development waste liquid containing TAA is greatly reduced.
如此,判明:通過上述專利文獻1記載的方法,可以獲得濃度比所通入的含有TAA離子的顯影廢液中的TAA離子濃度高的TAA鹽水溶液,但在有效地從含有TAA離子的顯影廢液中回收TAA離子的方面存在問題。As described above, it has been found that the TAA salt aqueous solution having a higher concentration of TAA ions in the developing waste liquid containing TAA ions can be obtained by the method described in Patent Document 1, but is effectively used from the development waste containing TAA ions. There is a problem in the recovery of TAA ions in the liquid.
此外,專利文獻2中記載的方法雖然使含有氫氧化TAA的顯影廢液串聯地流過多個吸附槽,但是所吸附的TAA離子的溶離對多個吸附槽同時進行。因此,雖然最初接觸該顯影廢液的吸附槽中的陽離子交換樹脂的交換率提高,但第二以後的吸附槽中的陽離子交換樹脂的交換率依然較低,在有效地從含有氫氧化TAA的顯影廢液中回收TAA離子的方面存在問題。Further, in the method described in Patent Document 2, the developing waste liquid containing TAA hydroxide is passed through a plurality of adsorption tanks in series, but the elution of the adsorbed TAA ions is simultaneously performed on the plurality of adsorption tanks. Therefore, although the exchange rate of the cation exchange resin in the adsorption tank initially contacting the development waste liquid is increased, the exchange rate of the cation exchange resin in the second and subsequent adsorption tanks is still low, effectively from the TAA containing hydroxide. There is a problem in the recovery of TAA ions in the developing waste liquid.
因此,本發明的目的在於提供一種TAA鹽水溶液的製造方法,其向填充有陽離子交換樹脂的填充塔中通入含有氫氧化TAA的顯影廢液,使TAA離子吸附於該樹脂,接著使樹脂與酸接觸,將被樹脂吸附的TAA離子溶離,獲得高濃度的TAA鹽水溶液,此時,可有效地製造高濃度的TAA鹽水溶液而不會使該顯影廢液中的TAA離子洩漏。Accordingly, an object of the present invention is to provide a method for producing a TAA salt aqueous solution in which a developing waste liquid containing TAA hydroxide is introduced into a packed column filled with a cation exchange resin, and TAA ions are adsorbed to the resin, followed by resin and The acid is contacted to dissolve the TAA ions adsorbed by the resin to obtain a high concentration of the TAA salt aqueous solution. At this time, a high concentration of the TAA salt aqueous solution can be efficiently produced without leaking the TAA ions in the developing waste liquid.
本發明人鑒於上述問題而進行了深入研究。首先,本發明人等向該填充塔中通入含有氫氧化TAA的顯影廢液,直至填充有使TAA離子吸附的陽離子交換樹脂的填充塔達到目標交換率(所吸附的TAA離子量相對於陽離子交換樹脂的總交換容量的比例)。此時,確認直至發生TAA離子從該填充塔的洩漏為止被該填充塔吸附的TAA離子量(“穿透容量”)、以及直至上述填充塔達到上述目標交換率為止的“TAA離子從填充塔洩漏的洩漏量”。The inventors conducted intensive studies in view of the above problems. First, the present inventors introduced a developing waste liquid containing TAA into the packed column until the packed column filled with the cation exchange resin for adsorbing TAA ions reached a target exchange rate (the amount of TAA ions adsorbed relative to the cation) The ratio of the total exchange capacity of the exchange resin). At this time, it is confirmed that the amount of TAA ions ("penetration capacity") adsorbed by the packed column until the TAA ion leaks from the packed column, and the "TAA ion from the packed column until the packed column reaches the target exchange rate" The amount of leakage leaked."
接著,準備與上述填充有陽離子交換樹脂的填充塔相同或基本相同的多個填充塔,將它們串聯連接來形成填充塔生產線,即使進行吸附處理直至通入顯影廢液一側的最上游的填充塔達到目標交換率,TAA離子也不會從最下游的填充塔洩漏,對這樣的填充塔的根數進行研究。Next, a plurality of packed columns identical or substantially identical to the packed column filled with the cation exchange resin described above are prepared, and they are connected in series to form a packed column production line, even if the adsorption process is performed until the most upstream filling on the side of the developing waste liquid. The tower reaches the target exchange rate, and the TAA ions do not leak from the most downstream packed tower. The number of such packed towers is studied.
結果發現,通過由上述的“TAA離子從填充塔洩漏的洩漏量”/“穿透容量”+1根(其中,小數點後進位)構成的填充塔生產線,可以進行吸附處理直至最上游的填充塔達到目標交換率而不會使TAA離子從最下游的填充塔洩漏。As a result, it was found that the adsorption tower can be subjected to the adsorption processing up to the most upstream filling by the packed column production line composed of the above-mentioned "Tail amount of leakage of TAA ions from the packed column" / "penetration capacity" + 1 (in which the decimal point is followed) The tower reaches the target exchange rate without leaking TAA ions from the most downstream packed column.
進而,獲得如下見解:與使用1個填充塔、向該填充塔中通入顯影廢液、在發生TAA離子洩漏時停止通入顯影廢液(在穿透容量下停止)來進行TAA離子的溶離的情況相比,在將前述目標交換率設定為超過填充塔的穿透容量的程度、從填充塔生產線上斷開達到了該目標交換率的最上游的填充塔、向被斷開的填充塔中通入酸水溶液來進行TAA離子的溶離的情況下,每根填充塔的TAA鹽水溶液的製造量大幅增加,可有效地獲得TAA鹽水溶液。Further, it has been found that the dissolution of TAA ions is carried out by using one packed column, introducing a developing waste liquid into the packed column, and stopping the passage of the developing waste liquid (stopping at the breakthrough capacity) when TAA ion leakage occurs. In the case of setting the target exchange rate to a level exceeding the penetration capacity of the packed column, the most upstream packed column that has reached the target exchange rate from the packed column production line, and the packed tower that has been disconnected When the acid aqueous solution is passed through to dissolve the TAA ions, the amount of the TAA salt aqueous solution per packed column is greatly increased, and the TAA salt aqueous solution can be efficiently obtained.
接著,將溶離TAA離子後的填充塔連接到以直接連接在上述最上游的填充塔的下游側的填充塔為最上游的填充塔生產線(剩餘填充塔生產線)的最下游,從而形成新的填充塔生產線。發現,透過使用該新的填充塔生產線,重複進行TAA離子的吸附工程和被吸附的TAA離子的溶離工程,可以用前述根數的填充塔效率良好地製造TAA鹽水溶液,從而完成以下本發明。Next, the packed column after dissolving the TAA ions is connected to the packed tower which is directly connected to the downstream side of the most upstream packed column as the most upstream of the packed tower production line (the remaining packed column production line), thereby forming a new filling. Tower production line. It has been found that by using the new packed column production line, the adsorption process of the TAA ions and the elution of the adsorbed TAA ions are repeated, and the TAA salt aqueous solution can be efficiently produced by the above-mentioned number of packed columns, thereby completing the following invention.
即,本發明為一種TAA鹽水溶液的製造方法,其包括如下工程:That is, the present invention is a method for producing a TAA salt aqueous solution, which comprises the following works:
吸附工程(S1),向初始填充塔生產線中通入含有氫氧化TAA而成的原料水溶液,使TAA離子吸附於陽離子交換樹脂,直至前述初始填充塔生產線的最上游的第一填充塔達到超過穿透容量的目標交換率,其中前述初始填充塔生產線由填充有陽離子交換樹脂的相同或基本相同的多個填充塔串聯連接而成;和In the adsorption engineering (S1), an aqueous solution of the raw material containing TAA hydroxide is introduced into the initial packed column production line to adsorb the TAA ions to the cation exchange resin until the first packed column at the most upstream of the initial packed column production line is over-pierced. a target exchange rate of the permeate capacity, wherein the aforementioned initial packed column production line is connected in series by a plurality of packed columns of the same or substantially the same filled with a cation exchange resin;
溶離再生工程(S2),從前述初始填充塔生產線上斷開通過前述吸附工程來吸附TAA離子至達到了目標交換率的前述第一填充塔,向該斷開的第一填充塔中通入酸水溶液,從而使所吸附的TAA離子以TAA鹽的水溶液的形式溶離,並且使被填充在前述第一填充塔中的陽離子交換樹脂再生;In the dissolution regeneration project (S2), the first packed column which adsorbs the TAA ions by the foregoing adsorption process to reach the target exchange rate is disconnected from the initial packed column production line, and the acid is introduced into the disconnected first packed column. An aqueous solution such that the adsorbed TAA ions are dissolved as an aqueous solution of the TAA salt, and the cation exchange resin filled in the aforementioned first packed column is regenerated;
使前述初始填充塔生產線中串聯連接的填充塔的數量為由下式(1)求得的整數n以上,從而使前述吸附工程中的前述初始填充塔生產線的最下游的填充塔的TAA離子吸附量低於穿透容量,The number of packed columns connected in series in the above-mentioned initial packed column production line is an integer n or more obtained by the following formula (1), so that the TAA ion adsorption of the packed column at the most downstream of the aforementioned initial packed column production line in the aforementioned adsorption process is performed. The amount is lower than the penetration capacity,
n={1+(直至第一填充塔達到目標交換率為止的TAA離子洩漏量(mol))/(第一填充塔的穿透容量(mol))}…(1)n={1+ (TAA ion leakage amount (mol) until the first packed column reaches the target exchange rate) / (penetration capacity (mol) of the first packed column)} (1)
其中小數點後進位,將前述溶離再生工程(S2)後得到再生的第一填充塔連接到將前述第一填充塔斷開後剩餘的剩餘填充塔生產線的最下游,形成以在前述吸附工程開始時直接連接在前述第一填充塔的下游側的第二填充塔為最上游的填充塔的、新的填充塔生產線,使用該新的填充塔生產線重複進行前述吸附工程(S3)和前述溶離再生工程(S4)。Wherein the decimal point is post-received, and the first packed column which is regenerated after the foregoing dissolution regeneration process (S2) is connected to the most downstream of the remaining packed column production line remaining after the first packed column is disconnected, and is formed to start at the foregoing adsorption process. The second packed column directly connected to the downstream side of the first packed column is the new packed column production line of the most upstream packed column, and the adsorption process (S3) and the aforementioned dissolution regeneration are repeated using the new packed column production line. Engineering (S4).
“相同或基本相同的多個填充塔”是指TAA離子的總交換容量相同或基本相同(總交換容量±10%、優選為±5%的差異)的填充塔。此外,形成本發明的填充塔生產線的多個填充塔為分別填充有相同陽離子交換樹脂、L/D相同的填充塔者為佳,較佳為全部相同的填充塔(陽離子交換樹脂的種類、填充量、所填充的柱相同)。"Multiple packed columns of the same or substantially the same" means a packed column in which the total exchange capacity of TAA ions is the same or substantially the same (the difference of the total exchange capacity ± 10%, preferably ± 5%). Further, it is preferable that the plurality of packed columns forming the packed column production line of the present invention are filled with the same cation exchange resin and the same packed column of L/D, and preferably all of the same packed columns (types of cation exchange resins, filling) The amount and the filled column are the same).
在上述發明中,將初始填充塔生產線的最上游的填充塔稱為第一填充塔、將直接連接在其下游側的填充塔稱為第二填充塔,在之後的吸附工程(S3)中的新的填充塔生產線中,最上游的填充塔為第二填充塔,在再之後的吸附工程(S4)中的新的填充塔生產線中,最上游的填充塔為第二填充塔的再下游側的填充塔。也就是說,本發明為重複進行如下處理的方法:一旦填充塔生產線的最上游的填充塔達到目標交換率,就將其斷開,形成以最近的下游側的填充塔為最上游的填充塔的剩餘填充塔生產線,將斷開的填充塔再生後,將其設置在上述剩餘填充塔生產線的最下游側,形成新的填充塔生產線,進行吸附工程。In the above invention, the packed tower which is the most upstream of the initial packed column production line is referred to as a first packed column, and the packed column directly connected to the downstream side thereof is referred to as a second packed column, and in the subsequent adsorption process (S3) In the new packed column production line, the most upstream packed column is the second packed column, and in the new packed column production line in the subsequent adsorption process (S4), the most upstream packed column is the further downstream side of the second packed column. The packed tower. That is, the present invention is a method of repeating the process of once the packed tower of the most upstream of the packed column production line reaches the target exchange rate, and is broken to form a packed tower having the most upstream packed side of the downstream side as the most upstream. The remaining packed tower production line, after the broken packed tower is regenerated, is placed on the most downstream side of the above remaining packed tower production line to form a new packed tower production line for adsorption engineering.
填充塔的“交換率”是指被填充塔吸附的TAA離子量(mol)相對於被填充在該填充塔中的陽離子交換樹脂的總交換容量(mol)的比例,“目標交換率”是指其目標值。The "exchange rate" of the packed column means the ratio of the amount of TAA ions (mol) adsorbed by the packed column to the total exchange capacity (mol) of the cation exchange resin filled in the packed column, and the "target exchange rate" means Its target value.
填充塔的“穿透容量”是指,僅向該填充塔供給原料水溶液,從該供給開始到TAA離子開始從該填充塔洩漏為止,被該填充塔中的陽離子交換樹脂吸附的TAA離子量(mol)。The "penetration capacity" of the packed column means that the raw material aqueous solution is supplied only to the packed column, and the amount of TAA ions adsorbed by the cation exchange resin in the packed column from the start of the supply until the TAA ion starts to leak from the packed column ( Mol).
填充塔的目標交換率超過穿透容量是指,將目標交換率設定得高於在填充塔達到穿透容量時的該填充塔的交換率。The target exchange rate of the packed column exceeds the breakthrough capacity, which means that the target exchange rate is set higher than the exchange rate of the packed column when the packed column reaches the breakthrough capacity.
另外,在上述TAA鹽水溶液的製造方法中,使構成前述初始填充塔生產線的填充塔的數量為前述整數n+1,在進行前述最上游的第一填充塔的溶離再生工程的期間,向斷開了該第一填充塔的剩餘填充塔生產線中通入原料溶液,在該剩餘填充塔生產線的最下游的填充塔的四烷基銨離子吸附量達到穿透容量之前,將再生了的第一填充塔連接到該剩餘填充塔生產線的最下游,由此,可以同時進行從吸附至達到了規定的目標交換率的填充塔溶離TAA離子、以及向填充塔生產線供給氫氧化TAA顯影廢液,可以連續地從含有氫氧化TAA的顯影廢液製造TAA鹽水溶液,是特佳的。Further, in the method for producing a TAA salt aqueous solution, the number of packed columns constituting the initial packed column production line is the integer n+1, and the separation is performed during the dissolution regeneration process of the first upstream packed column. a raw material solution is introduced into the remaining packed column production line of the first packed column, and the first amount of regeneration is obtained before the adsorption amount of the tetraalkylammonium ion of the packed column at the most downstream of the remaining packed column production line reaches the breakthrough capacity. The packed column is connected to the most downstream of the remaining packed column production line, whereby the packed column eluted TAA ions from the adsorption to the predetermined target exchange rate and the TATA developing waste liquid supplied to the packed column production line can be simultaneously performed, It is particularly preferable to continuously produce a TAA salt aqueous solution from a developing waste liquid containing TAA hydroxide.
另外,在上述TAA鹽水溶液的製造方法中,前述吸附工程的目標交換率為70~90%者為佳。在該目標交換率低於70%時,溶離工程中回收的TAA鹽溶液的濃度變稀,故為不佳,在該目標交換率超過90%時,擔心會在達到目標交換率為止所需的原料水溶液的供給量增大、處理成本上升,另外,擔心會形成初始填充塔生產線的填充塔的根數增大、生產成本(initial cost)上升。Further, in the method for producing a TAA salt aqueous solution, it is preferred that the target exchange rate of the adsorption process is 70 to 90%. When the target exchange rate is less than 70%, the concentration of the TAA salt solution recovered in the dissolution process becomes thin, so it is not good, and when the target exchange rate exceeds 90%, it is feared that it is required to reach the target exchange rate. The supply amount of the raw material aqueous solution is increased, the treatment cost is increased, and the number of packed columns that form the initial packed column production line is increased, and the initial cost is increased.
另外,在上述TAA鹽水溶液的製造方法中,較佳的是,前述溶離再生工程由直至排出所通入的酸水溶液的酸為止的第一溶離再生工程、和排出該酸以後的第二溶離再生工程組成,以該第一溶離再生工程中獲得的水溶液作為目標物即TAA鹽水溶液。如果所得TAA鹽水溶液中含有酸,則需要中和該酸的工程,處理效率會變差。因此,透過以由第一溶離再生工程獲得的不含酸的TAA鹽水溶液作為目標物,可以更有效地製造TAA鹽水溶液。Further, in the method for producing a TAA salt aqueous solution, it is preferred that the dissolution and regeneration process is performed by a first dissolution regeneration process until the acid of the acid aqueous solution that has been introduced, and a second dissolution regeneration after the acid is discharged. The engineering composition is obtained by using the aqueous solution obtained in the first dissolution regeneration project as the target TAA salt solution. If the obtained TAA salt aqueous solution contains an acid, the process of neutralizing the acid is required, and the treatment efficiency is deteriorated. Therefore, the TAA salt aqueous solution can be more efficiently produced by passing the acid-free TAA salt aqueous solution obtained by the first dissolution regeneration project as a target.
另外,在上述TAA鹽水溶液的製造方法中,可以利用監測排出液的導電率來進行前述溶離再生工程中的、從第一溶離再生工程到第二溶離再生工程的切換。Further, in the method for producing a TAA salt aqueous solution described above, the switching from the first dissolution regeneration process to the second dissolution regeneration process in the above-described dissolution regeneration process can be performed by monitoring the conductivity of the discharge liquid.
根據本發明,透過使用基於填充塔的穿透容量和TAA離子從該填充塔洩漏的洩漏量而確定根數的填充塔的方式,可以以高交換率進行TAA離子向填充塔的吸附而不會使TAA離子洩漏到從填充塔生產線的最下游的填充塔排出的排出液中。由此,可以提高每根填充塔的TAA鹽水溶液的製造量、有效地製造高濃度的TAA鹽水溶液。According to the present invention, by using a packing tower based on the breakthrough capacity of the packed column and the amount of leakage of TAA ions leaking from the packed column, the adsorption of TAA ions to the packed column can be performed at a high exchange rate without The TAA ions are leaked into the effluent discharged from the packed column at the most downstream of the packed column production line. Thereby, the production amount of the TAA salt aqueous solution per packed column can be increased, and a high concentration TAA salt aqueous solution can be efficiently produced.
另外,在本發明的TAA鹽水溶液的製造方法中,透過使用上述根數+1根的填充塔的方式,可以同時進行從吸附至達到了規定的目標交換率的填充塔溶離TAA離子、以及向填充塔生產線供給氫氧化TAA顯影廢液,可以連續地製造TAA鹽水溶液,進而可以效率良好地製造TAA鹽水溶液。Further, in the method for producing a TAA salt aqueous solution of the present invention, by using the above-described number of +1 packed columns, it is possible to simultaneously elute TAA ions from the adsorption tower to a packed column having a predetermined target exchange rate, and The TATA developing waste liquid is supplied to the packed column production line, and the TAA salt aqueous solution can be continuously produced, and the TAA salt aqueous solution can be efficiently produced.
進而,在本發明的製造方法中,對於串聯連接的所有填充塔,均使TAA離子吸附至達到相同的目標交換率為止再進行其溶離,因而可均等地使用各個填充塔中的陽離子交換樹脂。因此,可以期待填充塔中的陽離子交換樹脂的使用期限的長期化。Further, in the production method of the present invention, the TAA ions are adsorbed until they reach the same target exchange rate for all the packed columns connected in series, and the cation exchange resin in each packed column can be uniformly used. Therefore, it is expected that the life of the cation exchange resin in the packed column will be prolonged.
在本發明的TAA鹽水溶液的製造方法中,向填充塔生產線中通入含有氫氧化TAA而成的原料水溶液(以下,有時簡稱為“原料水溶液”。),使TAA離子吸附於該填充塔生產線中的陽離子交換樹脂。In the method for producing a TAA salt aqueous solution of the present invention, a raw material aqueous solution containing TAA hydroxide (hereinafter sometimes referred to simply as "raw material aqueous solution") is introduced into a packed column production line, and TAA ions are adsorbed to the packed column. Cation exchange resin in the production line.
上述原料水溶液中的氫氧化TAA是指,TAA離子的抗衡離子為氫氧化物離子的化合物,氫氧化TAA在原料水溶液中解離而以TAA離子和氫氧化物離子的狀態存在。作為上述氫氧化TAA,只要可在工業上得到就沒有特別限製,可以使用各種氫氧化TAA。作為該氫氧化TAA,例如可列舉出四甲基氫氧化銨、四乙基氫氧化銨、四丙基氫氧化銨、四丁基氫氧化銨等。在上述氫氧化TAA中,從廣泛用作半導體製造工程中的顯影液的觀點出發,可以適宜地使用四甲基氫氧化銨。The TAA of the above-mentioned raw material aqueous solution means a compound in which the counter ion of the TAA ion is a hydroxide ion, and the hydroxide TAA is dissociated in the raw material aqueous solution to exist in the state of TAA ion and hydroxide ion. The above-mentioned hydroxide TAA is not particularly limited as long as it can be industrially obtained, and various kinds of hydroxide TAA can be used. Examples of the hydroxide TAA include tetramethylammonium hydroxide, tetraethylammonium hydroxide, tetrapropylammonium hydroxide, and tetrabutylammonium hydroxide. Among the above-mentioned hydroxide TAA, tetramethylammonium hydroxide can be suitably used from the viewpoint of being widely used as a developer in a semiconductor manufacturing process.
另外,原料水溶液只要由氫氧化TAA的水溶液構成就沒有特別限製。作為原料水溶液,具體可列舉出由公知的製造方法獲得的氫氧化TAA水溶液、以及由半導體裝置(LSI、VLSI等)、印刷基板、液晶顯示器(LCD)等電子部件的製造工程中的顯影工程、洗滌工程排出的廢液(以下,有時分別稱為顯影工程廢液、洗滌工程廢液。)等。顯影工程廢液、洗滌工程廢液通常被混合而作為顯影廢液排放(以下,有時將顯影工程廢液與洗滌工程廢液的混合廢液稱為“顯影廢液”。)。在這些原料水溶液中,從可以通過本發明的TAA鹽的製造方法將該廢液中的TAA離子回收、再利用的觀點出發,適宜的是顯影廢液。Further, the raw material aqueous solution is not particularly limited as long as it is composed of an aqueous solution of TAA hydroxide. Specific examples of the raw material aqueous solution include a TAA aqueous solution obtained by a known production method, and a development process in a manufacturing process of an electronic component such as a semiconductor device (LSI, VLSI, etc.), a printed circuit board, or a liquid crystal display (LCD). The waste liquid discharged from the washing process (hereinafter, referred to as development waste liquid, washing waste liquid, etc., respectively). The development engineering waste liquid and the washing engineering waste liquid are usually mixed and discharged as development waste liquid (hereinafter, the mixed waste liquid of the development engineering waste liquid and the washing engineering waste liquid is sometimes referred to as "developing waste liquid"). In the aqueous solution of the raw material, the waste liquid can be developed from the viewpoint of recovering and recycling the TAA ions in the waste liquid by the method for producing a TAA salt of the present invention.
對於上述原料水溶液中的氫氧化TAA的濃度沒有特別限製,可以使用各種氫氧化TAA濃度的原料水溶液。例如,由前述顯影工程排出的顯影工程廢液中的氫氧化TAA的濃度通常為1.0~5.0質量%左右,而洗滌工程中使用顯影液的5~100倍的量的純水,因而產生大量的洗滌工程廢液,由於其與顯影工程廢液被混合,因此由半導體和液晶製造工程排出的顯影廢液中的氫氧化TAA濃度通常為100~10,000ppm左右。其中,由液晶顯示器製造工程排出的顯影廢液的氫氧化TAA濃度大多為100~5000ppm,本發明的製造方法特別適合於由這種氫氧化TAA濃度低的顯影廢液來製造TAA鹽水溶液。The concentration of the hydroxide TAA in the aqueous solution of the raw material is not particularly limited, and various aqueous raw material solutions having a TAA concentration of hydroxide can be used. For example, the concentration of TAA in the development waste liquid discharged from the development project is usually about 1.0 to 5.0% by mass, and the amount of pure water in the washing process is 5 to 100 times that of the developer, so that a large amount of Since the washing waste liquid is mixed with the development engineering waste liquid, the concentration of the TAA in the developing waste liquid discharged from the semiconductor and liquid crystal manufacturing engineering is usually about 100 to 10,000 ppm. Among them, the developing waste liquid discharged from the liquid crystal display manufacturing process has a TAA concentration of usually 100 to 5000 ppm, and the production method of the present invention is particularly suitable for producing a TAA salt aqueous solution from the developing waste liquid having a low TAA concentration.
在上述顯影廢液中含有從半導體‧液晶製造工程中從金屬層、管道材料等溶出的微量的金屬成分。對於上述金屬成分的濃度,例如,半導體製造工程中排出的含有氫氧化TAA的顯影廢液為0.1~50ppb,由液晶製造工程排出的含有氫氧化TAA的顯影廢液為1~100ppb左右。The developing waste liquid contains a trace amount of a metal component eluted from a metal layer, a pipe material, or the like from a semiconductor/liquid crystal manufacturing process. The concentration of the metal component is, for example, 0.1 to 50 ppb of the developing waste liquid containing TAA discharged in the semiconductor manufacturing process, and the developing waste liquid containing TAAA discharged by the liquid crystal manufacturing process is about 1 to 100 ppb.
另外,如前所述,上述顯影廢液中溶解有酚醛樹脂、聚苯乙烯樹脂等來源於光致抗蝕劑的有機物、以及微量的有機溶劑、表面活性劑等有機物(以下,有時將這些有機物總稱為“有機物”。)。溶解在氫氧化TAA濃度為1質量%以下的顯影廢液中的有機物的濃度通常按COD(化學需氧量)換算計為數ppm~數百ppm左右。In addition, as described above, an organic substance derived from a photoresist such as a phenol resin or a polystyrene resin, and a trace amount of an organic substance such as an organic solvent or a surfactant are dissolved in the developing waste liquid (hereinafter, these may be used) Organic matter is collectively referred to as "organic matter."). The concentration of the organic substance dissolved in the developing waste liquid having a TAA concentration of 1% by mass or less is usually in the range of several ppm to several hundreds ppm in terms of COD (chemical oxygen demand).
在本發明的TAA鹽水溶液的製造方法中,所使用的陽離子交換樹脂只要能吸附存在於原料水溶液中的TAA離子就沒有特別限製,可以使用可在工業上得到的陽離子交換樹脂。作為該陽離子交換樹脂,例如可列舉出:在苯乙烯-二乙烯基苯共聚物、丙烯酸-二乙烯基苯共聚物、甲基丙烯酸-二乙烯基苯共聚物等基體中導入了磺酸基等強酸基團的強酸性陽離子交換樹脂,以及在上述基體中導入了羧基、酚性羥基等弱酸基團的弱酸性陽離子交換樹脂。在這些陽離子交換樹脂中,從可以容易地脫附所吸附的TAA離子的觀點出發,使用弱酸性陽離子交換樹脂者為佳。In the method for producing a TAA salt aqueous solution of the present invention, the cation exchange resin to be used is not particularly limited as long as it can adsorb TAA ions present in the raw material aqueous solution, and an industrially obtainable cation exchange resin can be used. Examples of the cation exchange resin include a sulfonic acid group introduced into a matrix such as a styrene-divinylbenzene copolymer, an acrylic-divinylbenzene copolymer, or a methacrylic acid-divinylbenzene copolymer. A strongly acidic cation exchange resin of a strong acid group, and a weakly acidic cation exchange resin in which a weak acid group such as a carboxyl group or a phenolic hydroxyl group is introduced into the above matrix. Among these cation exchange resins, those which use a weakly acidic cation exchange resin are preferred from the viewpoint that the adsorbed TAA ions can be easily desorbed.
作為強酸性陽離子交換樹脂的具體例子,可列舉出Rohm and Haas公司製造的Amberlite IR120B、Amberlite IR124,三菱化學公司製造的DIAION SK1B、DIAION PK228,Sumika Chemtex Co.,Ltd.製造的Duolite C255LFH,LANXESS公司的LEWATIT MonoPlus S100,Purolite公司的Purolite C160等。另外,作為弱酸性陽離子交換樹脂的具體例子,可列舉出Rohm and Haas公司製造的Amberlite IRC76,三菱化學公司製造的DIAION WK40L,Sumika Chemtex Co.,Ltd.製造的Duolite C433LF、Duolite C476,LANXESS公司的LEWATIT CNP80WS,Purolite公司的Purolite C104等。Specific examples of the strongly acidic cation exchange resin include Amberlite IR120B manufactured by Rohm and Haas Co., Ltd., Amberlite IR124, DIAION SK1B manufactured by Mitsubishi Chemical Corporation, DIAION PK228, Duolite C255LFH manufactured by Sumika Chemtex Co., Ltd., and LANXESS Co., Ltd. LEWATIT MonoPlus S100, Purolite's Purolite C160 and so on. In addition, as a specific example of the weakly acidic cation exchange resin, Amberlite IRC76 manufactured by Rohm and Haas Co., Ltd., DIAION WK40L manufactured by Mitsubishi Chemical Corporation, Duolite C433LF manufactured by Sumika Chemtex Co., Ltd., Duolite C476, and LANXESS Co., Ltd. LEWATIT CNP80WS, Purolite C104 from Purolite.
另外,對於上述陽離子交換樹脂的結構也沒有特別限製,凝膠型、多孔型、高多孔型等中的任意一種結構的陽離子交換樹脂均可以適宜地使用。特別是從膨潤收縮強度優異的觀點出發,適宜為高多孔型。In addition, the structure of the cation exchange resin is not particularly limited, and any of the cation exchange resins of any of a gel type, a porous type, and a highly porous type can be suitably used. In particular, from the viewpoint of excellent swelling shrinkage strength, it is preferably a highly porous type.
上述陽離子交換樹脂通常以抗衡離子為氫離子(H型)或鈉離子(Na型)的形式在市場上銷售,但在使用Na型的陽離子交換樹脂時,通過與TAA離子的離子交換,會排出Na離子,存在含有TAA離子的排出液中的Na離子增加的傾向。因此,作為陽離子交換樹脂,優選使用H型。此外,在使用以Na型在市場上銷售的的陽離子交換樹脂的情況下,在使用時預先向陽離子交換樹脂中通入鹽酸、硫酸等酸來將抗衡離子轉換成H型後再使用即可。The above cation exchange resin is generally marketed as a counter ion in the form of a hydrogen ion (H type) or a sodium ion (Na type), but when a Na type cation exchange resin is used, it is discharged by ion exchange with TAA ions. The Na ion tends to increase in Na ions in the discharge liquid containing TAA ions. Therefore, as the cation exchange resin, H type is preferably used. Further, in the case of using a cation exchange resin which is commercially available as a Na type, an acid such as hydrochloric acid or sulfuric acid may be introduced into the cation exchange resin in advance to convert the counter ion into an H form and then used.
另外,上述H型的陽離子交換樹脂、以及通過酸將Na型轉換成H型的陽離子交換樹脂在與含有TAA離子的顯影廢液接觸之前,優選預先用超純水充分洗滌。Further, the above-mentioned H-type cation exchange resin and the cation exchange resin which converts the Na type to the H type by an acid are preferably washed in advance with ultrapure water before being brought into contact with the development waste liquid containing TAA ions.
從防止Na離子混入上述處理廢液中的觀點出發,在用超純水洗滌時,從上述陽離子交換樹脂排出的水中的鈉溶出量為100ppb以下者為佳。水中的鈉溶出量超過100ppb時,進行利用上述酸的通入的向H型的置換、以及利用超純水的洗滌直至水中的鈉溶出量為100ppb以下即可。From the viewpoint of preventing the incorporation of Na ions into the treatment waste liquid, it is preferred that the amount of sodium eluted from the water discharged from the cation exchange resin is 100 ppb or less when washing with ultrapure water. When the sodium elution amount in the water exceeds 100 ppb, the H-type substitution by the introduction of the above-mentioned acid and the washing with ultrapure water may be performed until the amount of sodium elution in the water is 100 ppb or less.
在本發明的TAA鹽水溶液的製造方法中,上述陽離子交換樹脂填充在填充塔中來使用。關於被填充在填充塔中的被轉換成H型的陽離子交換樹脂的高度(L)與樹脂塔的直徑(D)之比(L/D)、以及原料水溶液的通入速度,考慮陽離子交換樹脂的交換基的交換容量、原料水溶液中的氫氧化TAA濃度、或者TAA鹽水溶液的製造量等來適當確定即可。例如,如果是原料水溶液的氫氧化TAA濃度為0.001~1質量%的顯影廢液,則被填充在填充塔中的陽離子交換樹脂的高度(L)與樹脂塔的直徑(D)之比(L/D)在0.5~30、顯影廢液的空間速度(SV)在1~150h-1 的範圍適當設定即可。In the method for producing a TAA salt aqueous solution of the present invention, the cation exchange resin is used by being packed in a packed column. Regarding the ratio (L/D) of the height (L) of the cation exchange resin converted to H-type filled in the packed column to the diameter (D) of the resin column, and the rate of introduction of the aqueous solution of the raw material, consider the cation exchange resin. The exchange capacity of the exchange group, the TAA concentration of the hydroxide in the raw material aqueous solution, or the production amount of the TAA salt aqueous solution may be appropriately determined. For example, in the case of the developing waste liquid having a TAA concentration of 0.001 to 1% by mass of the aqueous solution of the raw material, the ratio of the height (L) of the cation exchange resin filled in the packed column to the diameter (D) of the resin column (L) /D) In 0.5 to 30, the space velocity (SV) of the developing waste liquid may be appropriately set in the range of 1 to 150 h -1 .
此外,隨著TAA離子向被填充在填充塔內的陽離子交換樹脂的吸附的進行,陽離子交換樹脂的體積膨潤,填充塔內的陽離子交換樹脂的高度增加。因此,考慮TAA離子被吸附至達到前述目標吸附率時的陽離子交換樹脂的體積來進行陽離子交換樹脂向填充塔的填充即可。Further, as the adsorption of TAA ions to the cation exchange resin filled in the packed column proceeds, the volume of the cation exchange resin swells, and the height of the cation exchange resin in the packed column increases. Therefore, it is sufficient to carry out the filling of the cation exchange resin into the packed column in consideration of the volume of the cation exchange resin when the TAA ions are adsorbed to the target adsorption rate.
此外,在原料水溶液為顯影廢液的情況下,如前所述,該顯影廢液中含有來源於抗蝕劑的樹脂等有機物。隨著該顯影廢液中的TAA離子被陽離子交換樹脂吸附,通過填充塔的顯影廢液的pH接近中性,隨著這種pH變化,上述有機物的溶解度降低,有時該有機物會析出在陽離子交換樹脂的表面和細孔中而殘留。Further, when the raw material aqueous solution is the development waste liquid, as described above, the development waste liquid contains an organic substance such as a resin derived from a resist. As the TAA ions in the developing waste liquid are adsorbed by the cation exchange resin, the pH of the developing waste liquid passing through the packed column is near neutral, and as the pH changes, the solubility of the organic substance is lowered, and sometimes the organic substance is precipitated in the cation. Remains in the surface of the resin and in the pores.
在該情況下,為了在使上述顯影廢液與填充有陽離子交換樹脂的填充塔接觸之後使有機物溶出,通過使堿與其接觸,可以溶解、洗滌所析出的有機物。如果如此在溶離再生工程前預先洗滌析出至陽離子交換樹脂的有機物,則添加酸將TAA離子從陽離子交換樹脂溶離而獲得的TAA鹽水溶液中的有機物的含量會變少,從獲得純度高的TAA鹽水溶液方面出發是特別優選的。In this case, in order to elute the organic waste after bringing the development waste liquid into contact with the packed column filled with the cation exchange resin, the precipitated organic matter can be dissolved and washed by bringing the rhodium into contact therewith. If the organic substance precipitated to the cation exchange resin is preliminarily washed before the dissolution regeneration process, the content of the organic substance in the aqueous solution of the TAA salt obtained by dissolving the TAA ion from the cation exchange resin is reduced, and the TAA salt having high purity is obtained. It is particularly preferred in terms of an aqueous solution.
此外,作為用於洗滌填充塔的上述堿,從避免金屬離子混入的觀點出發,優選使用氫氧化TAA溶液,特別是從避免雜質混入的觀點出發,使用含有與被陽離子交換樹脂吸附的TAA離子相同的TAA離子的氫氧化TAA水溶液者為佳。Further, as the above-mentioned crucible for washing the packed column, from the viewpoint of avoiding the incorporation of metal ions, it is preferred to use a TAA solution of hydroxide, particularly from the viewpoint of avoiding the incorporation of impurities, using the same TIA ion as that adsorbed by the cation exchange resin. The TAA ion of the aqueous solution of TAA is preferred.
被陽離子交換樹脂吸附的TAA離子可以通過使該樹脂與酸接觸而溶離。作為與該陽離子交換樹脂接觸的酸,只要是在水溶液的狀態下生成氫離子的物質就沒有特別限定,例如可例示出鹽酸、硫酸等的無機酸水溶液。在上述酸中,從可在工業上以廉價得到的觀點和易於調節濃度的觀點出發,鹽酸水溶液是最適宜的。對於上述鹽酸的濃度和用量,只要是足以將所吸附的TAA離子溶離的濃度和量就沒有特別限定,通常,使上述陽離子交換樹脂與1~20質量%的鹽酸水溶液以1~10(L/L-樹脂)接觸即足夠。The TAA ion adsorbed by the cation exchange resin can be dissolved by bringing the resin into contact with an acid. The acid to be contacted with the cation exchange resin is not particularly limited as long as it generates hydrogen ions in an aqueous solution, and examples thereof include inorganic acid aqueous solutions such as hydrochloric acid and sulfuric acid. Among the above acids, an aqueous hydrochloric acid solution is most suitable from the viewpoint of being industrially inexpensive to obtain and easy to adjust the concentration. The concentration and amount of the above hydrochloric acid are not particularly limited as long as it is sufficient to dissolve the adsorbed TAA ions. Usually, the cation exchange resin and the 1 to 20% by mass aqueous hydrochloric acid solution are 1 to 10 (L/). L-resin) contact is sufficient.
此外,接觸過酸的填充塔中的陽離子交換樹脂的抗衡離子變為H型,可以將再生後的該填充塔供於TAA離子的吸附工程而不特別進行該樹脂的洗滌。Further, the counter ion of the cation exchange resin in the packed column contacting the acid becomes H-type, and the regenerated packed column can be supplied to the adsorption process of the TAA ion without particularly washing the resin.
本發明的TAA鹽水溶液的製造方法的特徵在於,形成由填充有陽離子交換樹脂的相同或基本相同的多個填充塔串聯連接而成的初始填充塔生產線,使該初始填充塔生產線與前述原料水溶液接觸。The method for producing a TAA salt aqueous solution of the present invention is characterized in that an initial packed column production line in which a plurality of packed columns of the same or substantially the same filled with a cation exchange resin are connected in series is formed, and the initial packed column production line and the aforementioned raw material aqueous solution are formed. contact.
此外,“相同或基本相同的多個填充塔”是指TAA離子的總交換容量相同或基本相同(總交換容量±10%、優選為±5%的差異)的填充塔。此外,形成本發明的填充塔生產線的多個填充塔較佳為分別填充有相同的陽離子交換樹脂、L/D相同的填充塔,從填充塔生產線的管理變得簡便的觀點出發,更佳為全部相同的填充塔(陽離子交換樹脂的種類、填充量、所填充的柱相同)。Further, "a plurality of packed columns which are the same or substantially the same" means a packed column in which the total exchange capacity of TAA ions is the same or substantially the same (the difference of the total exchange capacity ± 10%, preferably ± 5%). Further, it is preferable that a plurality of packed columns forming the packed column production line of the present invention are filled with the same cation exchange resin and a packed column having the same L/D, and it is more preferable from the viewpoint of simple management of the packed column production line. All the same packed columns (the type of cation exchange resin, the amount of the cation exchange, and the packed column are the same).
另外,如後所述,使用上述初始填充塔生產線,如後面說明的那樣重複進行原料水溶液中的TAA離子的吸附、脫離時,由於填充塔內的一部分陽離子交換樹脂劣化等,有時在各個填充塔之間總交換容量會出現差異(根據情況,有時會產生±10%以上的差異。),在這種情況下,也將各填充塔視為基本相同。In addition, as described later, when the adsorption and detachment of TAA ions in the raw material aqueous solution are repeated as described later, the cation exchange resin in the packed column is deteriorated, and sometimes in each filling. There is a difference in the total exchange capacity between the towers (depending on the situation, sometimes a difference of ±10% or more is generated.) In this case, each packed tower is also considered to be substantially the same.
在這裡,填充塔的TAA離子的交換率表示,相對於被填充在填充塔中的陽離子交換樹脂的總交換容量,該樹脂的抗衡離子由H型被轉換成TAA型的比例,可以由下式(2)求出。Here, the exchange rate of the TAA ions of the packed column indicates the ratio of the counter ion of the resin converted from the H type to the TAA type with respect to the total exchange capacity of the cation exchange resin filled in the packed column, and can be expressed by the following formula (2) Find.
{(與填充塔接觸的氫氧化TAA的總量(mol))-(從填充塔排出的TAA離子量(mol))}/(被填充在填充塔中的陽離子交換樹脂的總交換容量(mol))…(2){(Total amount of hydroxide TAA in contact with the packed column) - (Amount of TAA ion (mol) discharged from the packed column)} / (Total exchange capacity of the cation exchange resin filled in the packed column (mol ))…(2)
式(2)中,與填充塔接觸的氫氧化TAA的總量可以由原料水溶液中的氫氧化TAA的摩爾濃度和該溶液向填充塔的供給量來算出。另外,從填充塔排出的TAA離子量可以通過用離子色譜分析從填充塔排出的排出液中的TAA離子濃度來求出。In the formula (2), the total amount of the TAA in contact with the packed column can be calculated from the molar concentration of the hydroxide TAA in the raw material aqueous solution and the supply amount of the solution to the packed column. Further, the amount of TAA ions discharged from the packed column can be determined by analyzing the concentration of TAA ions in the discharged liquid discharged from the packed column by ion chromatography.
接著,在本發明的製造方法中,將位於上述填充塔生產線的最上游的填充塔、即初始填充塔生產線中的第一填充塔的目標交換率設定為超過第一填充塔的穿透容量的程度,向上述填充塔生產線中通入原料水溶液,直至達到該目標交換率。在向填充塔中通入原料水溶液直至超過了該填充塔的穿透容量的情況下,TAA離子會流出到排出液中。在本發明中,如下面所說明的那樣,通過串聯運接規定數量n的填充塔來形成填充塔生產線,可以防止TAA離子流出到排出液中而有效地吸附TAA離子、有效地製造TAA鹽水溶液。Next, in the manufacturing method of the present invention, the target exchange rate of the first packed column in the most upstream packed column of the packed column production line, that is, the first packed column in the initial packed column production line is set to exceed the breakthrough capacity of the first packed column. To the extent that the raw material aqueous solution is passed into the above-mentioned packed column production line until the target exchange rate is reached. In the case where the raw material aqueous solution is introduced into the packed column until the breakthrough capacity of the packed column is exceeded, the TAA ions flow out into the discharged liquid. In the present invention, as described below, by forming a packed column production line by serially transporting a predetermined number n of packed columns, it is possible to prevent TAA ions from flowing out into the discharge liquid, effectively adsorbing TAA ions, and efficiently producing TAA salt aqueous solution. .
此外,上述目標交換率設定為70~90%者為佳。在目標交換率低於70%時,溶離工程中回收的TAA鹽水溶液的濃度變稀。另外,隨著TAA離子的交換率提高,陽離子交換樹脂的吸附效率、即供給於填充塔的原料水溶液中的TAA離子被陽離子交換樹脂吸附的比例降低,存在TAA離子的洩漏量迅速增加的傾向。因此,在目標交換率超過90%時,不僅會擔心在達到目標交換率為止所需的原料水溶液的供給量增大、原料水溶液的處理成本上升,而且為了防止TAA離子從最下游的填充塔洩漏,形成初始填充塔生產線的填充塔的根數會增大、原始成本會上升。尤其,從原料水溶液的處理成本和用於形成初始填充塔生產線的原始成本的觀點出發,在80~90%的範圍設定上述目標交換率者為佳。In addition, it is preferable that the above target exchange rate is set to 70 to 90%. When the target exchange rate is less than 70%, the concentration of the TAA salt aqueous solution recovered in the dissolution process becomes thin. In addition, as the exchange rate of TAA ions increases, the adsorption efficiency of the cation exchange resin, that is, the ratio of the TAA ions supplied to the raw material aqueous solution of the packed column to the cation exchange resin decreases, and the amount of leakage of TAA ions tends to increase rapidly. Therefore, when the target exchange rate exceeds 90%, not only the supply amount of the raw material aqueous solution required to reach the target exchange rate is increased, the treatment cost of the raw material aqueous solution is increased, but also the TAA ion is prevented from leaking from the most downstream packed column. The number of packed towers that form the initial packed tower production line will increase and the original cost will increase. In particular, from the viewpoint of the treatment cost of the raw material aqueous solution and the original cost for forming the initial packed column production line, it is preferable to set the above target exchange rate in the range of 80 to 90%.
將來自初始填充塔生產線的最上游的填充塔的排出液依次通入串聯連接到該填充塔的第二以後的填充塔。因此,在來自最上游的填充塔的排出液中含有TAA離子時,該排出液中的TAA離子依次被填充在第二以後的填充塔中的陽離子交換樹脂吸附。本發明的製造方法的特徵在於,使形成初始填充塔生產線的填充塔的根數為由下式(1)求出的整數n以上(其中,在由該式求出的值不為整數時,小數點後進位元取整。)。The effluent from the most upstream packed column of the initial packed column line is passed sequentially into a second and subsequent packed column connected in series to the packed column. Therefore, when TAA ions are contained in the discharged liquid from the most upstream packed column, the TAA ions in the discharged liquid are sequentially adsorbed by the cation exchange resin filled in the second and subsequent packed columns. In the production method of the present invention, the number of the packed columns forming the initial packed column production line is an integer n or more obtained by the following formula (1) (wherein, when the value obtained by the formula is not an integer) The decimal point is rounded up after the decimal point.).
n={1+(直至第一填充塔達到目標交換率為止的從該第一填充塔洩漏的TAA離子的量(mol))/(第一填充塔的穿透容量(mol))}…(1)n={1+ (amount (mol) of TAA ions leaking from the first packed column until the first packed column reaches the target exchange rate) / (penetration capacity (mol) of the first packed column)}... 1)
通過使形成初始填充塔生產線的填充塔的根數為上述根數(n以上),可以進行TAA離子的吸附處理直至最上游的填充塔的TAA離子的交換率達到上述目標交換率而TAA離子不會從最下游的填充塔洩漏。By setting the number of the packed columns forming the initial packed column production line to the above number (n or more), the adsorption treatment of the TAA ions can be performed until the exchange rate of the TAA ions of the most upstream packed column reaches the above target exchange rate and the TAA ions are not It will leak from the most downstream packed tower.
形成初始填充塔生產線的填充塔的根數只要為上述整數n以上就沒有特別限製,考慮製造裝置的大小等來適當確定即可。然而,如果填充塔的根數過多,則在一次的TAA離子的吸附工程中不參與TAA離子的吸附的填充塔會增加,在工業上稱不上有效,因而形成填充塔生產線的填充塔的根數優選在上述整數n~n+2的範圍適當設定。The number of the packed columns forming the initial packed column production line is not particularly limited as long as it is the above-described integer n or more, and may be appropriately determined in consideration of the size of the production apparatus and the like. However, if the number of packed columns is too large, the packed column which does not participate in the adsorption of TAA ions in the adsorption process of the primary TAA ions will increase, which is not industrially effective, and thus forms the root of the packed column of the packed column production line. The number is preferably set as appropriate in the range of the above integer n~n+2.
尤其,在使填充塔生產線的根數為n+1的情況下,如後所述,可以同時進行達到了規定的目標交換率的填充塔的溶離再生工程、和向剩餘填充塔生產線供給原料水溶液的吸附工程。因此,可以連續地進行原料水溶液的處理,可以連續地製造TAA鹽水溶液,故特別優選。In particular, when the number of the packed column production lines is n+1, as described later, the dissolution regeneration process of the packed column which has reached the predetermined target exchange rate and the supply of the raw material aqueous solution to the remaining packed column production line can be simultaneously performed. Adsorption engineering. Therefore, the treatment of the raw material aqueous solution can be continuously performed, and the TAA salt aqueous solution can be continuously produced, which is particularly preferable.
在這裡,填充塔的“穿透容量”是指,向該填充塔供給原料水溶液,從該供給開始到TAA離子開始從該填充塔洩漏為止,被該填充塔中的陽離子交換樹脂吸附的TAA離子量(mol)。Here, the "penetration capacity" of the packed column means that the raw material aqueous solution is supplied to the packed column, and the TAA ion adsorbed by the cation exchange resin in the packed column from the start of the supply until the TAA ion starts to leak from the packed column. Amount (mol).
第一填充塔的穿透容量(mol)、和直至該第一填充塔達到目標交換率為止從該第一填充塔洩漏的TAA離子的量(mol)可以通過以下方法求出。The penetration capacity (mol) of the first packed column and the amount (mol) of TAA ions leaking from the first packed column until the first packed column reaches the target exchange rate can be obtained by the following method.
最初,準備與形成初始填充塔生產線的填充塔相同或基本相同的填充塔,向該填充塔供給原料水溶液。這裡使用的原料水溶液可以沒有特別限製地使用上述原料水溶液。Initially, a packed column identical or substantially identical to the packed column forming the initial packed column production line is prepared, and an aqueous raw material solution is supplied to the packed column. The aqueous raw material solution used herein can be used without any particular limitation.
此外,在使用上述顯影廢液作為原料水溶液的情況下,由於該顯影廢液中含有的金屬離子的存在,因而會擔心無法準確求得前述穿透容量和TAA離子洩漏量。然而,如前所述,顯影廢液中的金屬離子相對於氫氧化TAA的比例不過為1%以下,可以忽略顯影廢液中的金屬離子的存在。因此,作為用於確定上述穿透容量和TAA離子洩漏量的原料水溶液,即使使用該顯影廢液也沒有任何問題。Further, when the above-mentioned developing waste liquid is used as the raw material aqueous solution, there is a fear that the above-mentioned penetration capacity and TAA ion leakage amount cannot be accurately obtained due to the presence of metal ions contained in the development waste liquid. However, as described above, the ratio of the metal ions in the developing waste liquid to the TAA hydroxide is not more than 1%, and the presence of metal ions in the developing waste liquid can be ignored. Therefore, as the raw material aqueous solution for determining the above-described penetration capacity and TAA ion leakage amount, there is no problem even if the development waste liquid is used.
向填充塔供給上述原料水溶液,隨時間對從填充塔排出的排出液進行取樣,通過離子色譜來分析該排出液中的TAA離子濃度。可以通過直至第一次在排出液中檢出TAA離子的時刻為止供給到填充塔中的原料水溶液量和該原料水溶液的TAA離子的摩爾濃度來算出穿透容量。另外,也可以通過前述式(2)求出該填充塔中的陽離子交換樹脂的交換率。進而,繼續通入原料水溶液的和分析排出液,直至填充塔中的陽離子交換樹脂的交換率達到目標交換率,可以通過分析達到目標交換率的時刻的排出液來求出上述TAA離子洩漏量。The raw material aqueous solution was supplied to the packed column, and the discharged liquid discharged from the packed column was sampled over time, and the concentration of TAA ions in the discharged liquid was analyzed by ion chromatography. The penetration capacity can be calculated from the amount of the raw material aqueous solution supplied to the packed column and the molar concentration of the TAA ion in the raw material aqueous solution up to the time when the TAA ion is detected in the discharged liquid for the first time. Further, the exchange rate of the cation exchange resin in the packed column can also be determined by the above formula (2). Further, the introduction of the raw material aqueous solution and the analysis of the discharged liquid are continued until the exchange rate of the cation exchange resin in the packed column reaches the target exchange rate, and the TAA ion leakage amount can be obtained by analyzing the discharge liquid at the time when the target exchange rate is reached.
本發明的TAA鹽水溶液的製造方法,其包括如下工程:吸附工程,向由透過上述方法求得的根數形成的初始填充塔生產線中通入前述原料水溶液,使TAA離子吸附於位於該填充塔生產線的最上游的第一填充塔直至達到目標交換率;和溶離再生工程,從前述初始填充塔生產線上斷開通過該吸附工程吸附了規定量的TAA離子的該第一填充塔,向該第一填充塔中通入酸水溶液,從而使所吸附的TAA離子以TAA鹽的水溶液的形式溶離,並且使被填充在該第一填充塔的陽離子交換樹脂再生;該方法使前述吸附工程中的前述初始填充塔生產線的最下游的填充塔的TAA離子吸附量低於穿透容量,將前述溶離再生工程後得到再生的第一填充塔連接到從初始填充塔生產線上斷開第一填充塔而剩餘的剩餘填充塔生產線的最下游,形成以直接連接在第一填充塔的下游側的第二填充塔為最上游的填充塔的、新的填充塔生產線,用該新的填充塔生產線重複進行吸附工程和溶離再生工程。The method for producing a TAA salt aqueous solution of the present invention comprises the following steps: adsorption engineering, introducing an aqueous solution of the raw material into an initial packed column production line formed by the number obtained by the above method, and adsorbing TAA ions in the packed tower. a first packed column upstream of the production line until the target exchange rate is reached; and a dissolution regeneration process, the first packed column in which a predetermined amount of TAA ions are adsorbed by the adsorption process is disconnected from the initial packed column production line, to the first An acid aqueous solution is introduced into a packed column to dissolve the adsorbed TAA ions in the form of an aqueous solution of the TAA salt, and to regenerate the cation exchange resin filled in the first packed column; the method enables the aforementioned adsorption engineering The TAA ion adsorption amount of the packed column at the most downstream of the initial packed column production line is lower than the breakthrough capacity, and the first packed column which is regenerated after the foregoing dissolution regeneration process is connected to the first packed column which is disconnected from the initial packed column production line. The most downstream of the remaining packed column production line, forming a second packed column directly connected to the downstream side of the first packed column Upstream of the packed column, packed column new production line, works are repeated adsorption and regeneration engineering eluting the new packed column lines.
以下,對於本發明的製造方法,基於圖2來說明優選的方式,但本發明的製造方法並不限定於圖2的方式。圖2為在使各填充塔的目標交換率為80%、由前述式(1)求得的整數n為2的情況下用2根填充塔形成初始填充塔生產線時的流程圖。Hereinafter, a preferred embodiment will be described with reference to Fig. 2 for the manufacturing method of the present invention, but the manufacturing method of the present invention is not limited to the embodiment of Fig. 2 . 2 is a flow chart when the initial packed column production line is formed by using two packed columns in the case where the target exchange rate of each packed column is 80% and the integer n obtained by the above formula (1) is 2.
在圖2中,以初始填充塔生產線的第一填充塔為(A)塔、以第二填充塔為(B)塔來表示。首先,從初始填充塔生產線的(A)塔側通入原料水溶液,持續通液直至(A)塔的TAA離子的吸附達到目標交換率為止(TAA離子的吸附工程)。從(A)塔排出的排出液通入串聯連接的下游的(B)塔。此時,(B)塔的TAA離子的交換量為穿透容量以下,因此TAA離子不會洩漏到從(B)塔排出的排出液中(步驟1)。In Figure 2, the first packed column of the initial packed column line is (A) and the second packed column is (B). First, an aqueous raw material solution was passed from the (A) column side of the initial packed column production line, and the liquid was continuously supplied until the adsorption of the TAA ions of the (A) column reached the target exchange rate (TAA ion adsorption engineering). The discharged liquid discharged from the (A) column is passed to the (B) column downstream of the series connection. At this time, since the exchange amount of the TAA ions in the (B) column is equal to or less than the breakthrough capacity, the TAA ions do not leak into the discharged liquid discharged from the (B) column (step 1).
接著,從初始填充塔生產線上斷開(A)塔,向(A)塔中通入酸水溶液,進行TAA離子的溶離,將TAA離子以TAA氯化物水溶液的形式回收。此時,(B)塔作為剩餘填充塔生產線待命(步驟2)。Next, the (A) column was disconnected from the initial packed column production line, and an aqueous acid solution was introduced into the (A) column to elute the TAA ions, and the TAA ions were recovered as a TAA chloride aqueous solution. At this time, the (B) column is standby as the remaining packed column production line (step 2).
結束了TAA離子的溶離的(A)塔的陽離子交換樹脂的抗衡離子變成H型,(A)塔的再生工程與TAA離子的溶離一同結束。在此,溶離再生工程結束後的(A)塔連接到作為剩餘填充塔生產線的(B)塔的最下游,形成以(B)塔為第一填充塔的、新的填充塔生產線。接著,向(B)塔中通入原料水溶液直至(B)塔的TAA離子的吸附達到目標交換率,進行利用新的填充塔生產線的TAA離子的吸附工程(步驟3)。The counter ion of the cation exchange resin of the (A) column in which the TAA ion is dissolved is changed to the H type, and the regeneration process of the (A) column is completed together with the dissolution of the TAA ion. Here, the (A) column after the completion of the dissolution regeneration process is connected to the most downstream of the (B) column which is the remaining packed column production line, and a new packed column production line in which the (B) column is the first packed column is formed. Next, the raw material aqueous solution is introduced into the (B) column until the adsorption of the TAA ions in the (B) column reaches the target exchange rate, and the adsorption process of the TAA ions by the new packed column production line is performed (step 3).
步驟3的吸附工程後,從該填充塔生產線上斷開(B)塔,向(B)塔中通入酸水溶液,進行TAA離子的溶離,回收TAA氯化物水溶液。此時,(A)塔作為剩餘填充塔生產線待命(步驟4)。After the adsorption process of the step 3, the (B) column is disconnected from the packed column production line, and an aqueous acid solution is introduced into the (B) column to elute the TAA ions, and the TAA chloride aqueous solution is recovered. At this time, the (A) column is standby as the remaining packed column production line (step 4).
如此,透過重複進行上述步驟1~4,可以使用2根填充塔來效率良好地製造TAA鹽水溶液。Thus, by repeating the above steps 1 to 4, it is possible to efficiently produce a TAA salt aqueous solution using two packed columns.
另外,在本發明的TAA鹽水溶液的製造方法中,透過使形成上述填充塔生產線的填充塔的根數為n+1,可以在進行上述溶離再生工程的期間向剩餘填充塔生產線中通入原料溶液,並在該剩餘填充塔生產線的最下游的填充塔的TAA離子吸附量達到該最下游的填充塔的穿透容量之前將得到再生的填充塔連接到該剩餘填充塔生產線的最下游,由此,可以各自同時進行達到了目標交換率的最上游的填充塔的溶離再生工程、和基於向剩餘填充塔生產線供給原料水溶液的吸附工程,可以連續地製造TAA鹽水溶液。Further, in the method for producing a TAA salt aqueous solution of the present invention, the number of the packed columns forming the packed column production line is n+1, and the raw material can be introduced into the remaining packed column production line during the above-described dissolution regeneration process. a solution, and connecting the regenerated packed column to the most downstream of the remaining packed column line before the TAA ion adsorption amount of the packed column at the most downstream of the remaining packed column production line reaches the breakthrough capacity of the most downstream packed column In this way, the dissolution regeneration process of the most upstream packed column that has reached the target exchange rate and the adsorption process based on the supply of the raw material aqueous solution to the remaining packed column production line can be performed simultaneously, and the TAA salt aqueous solution can be continuously produced.
以下,對於由n+1根的填充塔形成初始填充塔生產線的本發明的TAA鹽水溶液的製造方法,基於圖3來進行說明,但該圖3不過是本發明的一個方式的例示,本發明不限定於圖3的方式。Hereinafter, a method for producing a TAA salt aqueous solution of the present invention in which an initial packed column production line is formed by n+1 packed columns will be described based on Fig. 3, but Fig. 3 is merely an illustration of one embodiment of the present invention, and the present invention It is not limited to the mode of FIG.
圖3與圖2同樣,是在使各填充塔的目標交換率為80%、由前述式(1)求得的整數n為2的情況下的流程圖,由2+1根、即3根填充塔形成填充塔生產線。3 is a flowchart in the case where the target exchange rate of each packed column is 80% and the integer n obtained by the above formula (1) is 2, which is 2+1, that is, 3 The packed tower forms a packed tower production line.
在圖3中,以初始填充塔生產線的第一填充塔為(A)塔、以其後的填充塔分別為(B)塔、(C)塔。與上述圖2同樣,向初始填充塔生產線的(A)塔中通入原料水溶液,進行TAA離子的吸附工程,直至(A)塔的TAA離子的吸附達到目標交換率。從(A)塔排出的排出液通入串聯連接的(B)塔。此時,(B)塔的TAA離子的交換量為穿透容量以下,TAA離子不會洩漏到從(B)塔排出的排出液中。因此,(C)塔先待命(步驟1)。此外,即使向C塔中通入來自(B)塔的排出液也沒有任何問題。In Fig. 3, the first packed column in the initial packed column production line is the (A) column, and the subsequent packed columns are the (B) column and the (C) column, respectively. In the same manner as in the above-mentioned FIG. 2, the raw material aqueous solution was introduced into the (A) column of the initial packed column production line, and the TAA ion adsorption process was performed until the adsorption of the TAA ions of the (A) column reached the target exchange rate. The discharged liquid discharged from the (A) column is passed to the (B) column connected in series. At this time, the exchange amount of the TAA ions in the (B) column is equal to or less than the breakthrough capacity, and the TAA ions are not leaked into the discharge liquid discharged from the (B) column. Therefore, the (C) tower is on standby (step 1). Further, there is no problem even if the discharge liquid from the (B) column is introduced into the C column.
接著,從初始填充塔生產線上斷開(A)塔,向(A)塔中通入酸水溶液,進行TAA離子的脫離,將TAA離子以TAA氯化物水溶液的形式回收。同時,向由(B)塔-(C)塔形成的、以(B)塔為最上游的新的填充塔生產線中通入原料水溶液,進行TAA離子的吸附工程,直至(B)塔的TAA離子的吸附達到目標交換率。此時,(C)塔的TAA離子的交換量為穿透容量以下,TAA離子不會洩漏到從(C)塔排出的排出液中。另外,結束了TAA離子的溶離的(A)塔的陽離子交換樹脂的抗衡離子變成H型,(A)塔的再生工程與TAA離子的溶離一同結束(步驟2)。Next, the (A) column was disconnected from the initial packed column production line, and an aqueous acid solution was introduced into the (A) column to remove the TAA ions, and the TAA ions were recovered as a TAA chloride aqueous solution. At the same time, a raw material aqueous solution is introduced into the new packed column production line formed by the (B) column-(C) column and the (B) column is the most upstream, and the TAA ion adsorption process is performed until the (TA) TAA of the column (B) The adsorption of ions reaches the target exchange rate. At this time, the exchange amount of the TAA ions in the (C) column is equal to or less than the breakthrough capacity, and the TAA ions are not leaked into the discharge liquid discharged from the (C) column. Further, the counter ion of the cation exchange resin of the (A) column in which the TAA ion is dissolved is changed to the H type, and the regeneration process of the (A) column is completed together with the dissolution of the TAA ion (step 2).
步驟2結束後,從填充塔生產線上斷開(B)塔,向(B)塔中通入酸水溶液,進行TAA離子的溶離,將TAA離子以TAA氯化物水溶液的形式回收。同時,向由(C)塔-(A)塔形成的、以(C)塔為最上游的新的填充塔生產線中通入原料水溶液,進行TAA離子的吸附工程,直至(C)塔的TAA離子的吸附達到目標交換率。此時,(A)塔的TAA離子的交換量為穿透容量以下,TAA離子不會洩漏到從(A)塔排出的排出液中。另外,結束了TAA離子的溶離的(B)塔的陽離子交換樹脂的抗衡離子變成H型,(B)塔的再生工程與TAA離子的溶離一同結束(步驟3)。After the completion of the step 2, the (B) column is disconnected from the packed column production line, and an acid aqueous solution is introduced into the (B) column to elute the TAA ions, and the TAA ions are recovered as a TAA chloride aqueous solution. At the same time, a raw material aqueous solution is introduced into the new packed column production line formed by the (C) column-(A) column and the (C) column is the most upstream, and the TAA ion adsorption process is performed until the (C) tower TAA The adsorption of ions reaches the target exchange rate. At this time, the exchange amount of the TAA ions in the (A) column is equal to or less than the breakthrough capacity, and the TAA ions are not leaked into the discharge liquid discharged from the (A) column. Further, the counter ion of the cation exchange resin of the (B) column in which the TAA ion is dissolved is changed to the H type, and the regeneration process of the (B) column is completed together with the dissolution of the TAA ion (step 3).
步驟3結束後,從填充塔生產線上斷開(C)塔,向(C)塔中通入酸水溶液,進行TAA離子的溶離,將TAA離子以TAA氯化物水溶液的形式回收。同時,向由(A)塔-(B)塔形成的、以(A)塔為最上游的新的填充塔生產線中通入原料水溶液,進行TAA離子的吸附工程,直至(A)塔的TAA離子的吸附達到目標交換率(步驟4)。After the end of step 3, the (C) column is disconnected from the packed column production line, and an acid aqueous solution is introduced into the (C) column to elute the TAA ions, and the TAA ions are recovered as a TAA chloride aqueous solution. At the same time, a raw material aqueous solution is introduced into the new packed column production line formed by the (A) column-(B) column and the (A) column is the most upstream, and the TAA ion adsorption process is performed until the TAA of the (A) column. The adsorption of ions reaches the target exchange rate (step 4).
以下,通過重複進行步驟2~4,可以同時進行從吸附TAA離子至達到了規定的目標交換率的各填充塔溶離TAA離子的溶離再生工程、和向各填充塔生產線供給原料水溶液的吸附工程,可以連續地製造TAA鹽水溶液。In the following, by repeating steps 2 to 4, it is possible to simultaneously perform an elution regeneration process in which TAA ions are eluted from each of the packed towers that have reached a predetermined target exchange rate, and an adsorption process in which a raw material aqueous solution is supplied to each packed column production line. The TAA salt aqueous solution can be continuously produced.
在本發明的四烷基銨鹽水溶液的製造方法中,可以將溶離再生工程分為二個階段進行。如上所述,溶離再生工程為如下工程:在填充塔生產線的上游側的填充塔吸附TAA離子至達到了目標交換率時,從填充塔生產線上斷開該上游側的填充塔,向該斷開的填充塔中通入酸水溶液,從而將該填充塔所吸附的TAA離子以TAA鹽水溶液的形式溶離。In the method for producing a tetraalkylammonium salt aqueous solution of the present invention, the dissolution regeneration process can be carried out in two stages. As described above, the dissolution regeneration process is a process in which, when the packed column on the upstream side of the packed column production line adsorbs TAA ions until the target exchange rate is reached, the packed column on the upstream side is disconnected from the packed column production line, and the disconnection is performed. An aqueous acid solution is introduced into the packed column to dissolve the TAA ions adsorbed by the packed column in the form of an aqueous TAA salt solution.
圖4為在溶離再生工程中在使填充塔的目標交換率為80%的情況下測定的相對於排出液的容量的、排出液中的HCl濃度和TAA鹽(四甲基氯化銨:TMACl)濃度的圖表。根據圖4,首先只有TMACl溶離,然後,開始流出HCl而流出TMACl與HCl的混合溶液。Figure 4 is a graph showing the HCl concentration in the effluent and the TAA salt (tetramethylammonium chloride: TMACl) measured in the dissolution regeneration process with the target exchange rate of the packed column at 80%. ) The chart of concentration. According to Fig. 4, only TMACl was first dissolved, and then, HCl was started to flow out and a mixed solution of TMACl and HCl was flowed out.
排出液中含有HCl時,需要中和該排出液,工程會增加,故不佳。因此,在本發明的較佳方式中,將溶離再生工程分為直至開始排出所通入的酸水溶液的酸為止的第一溶離再生工程、和開始排出酸以後的第二溶離再生工程這兩個,以通過第一溶離再生工程獲得的不含酸的排出液作為目標物即TAA鹽水溶液。此外,從第二溶離再生工程排出的含有酸和TAA鹽的水溶液可以用作之後的溶離再生工程中使用的酸水溶液,由此,可以不浪費地分取再生了的TAA鹽。When HCl is contained in the effluent, it is necessary to neutralize the effluent, and the engineering will increase, which is not preferable. Therefore, in a preferred embodiment of the present invention, the dissolution regeneration process is divided into a first dissolution regeneration process until the start of the acid of the introduced acid aqueous solution, and a second dissolution regeneration process after the start of the discharge of the acid. The acid-free effluent obtained by the first dissolution regeneration project was used as a target, that is, a TAA salt aqueous solution. Further, the aqueous solution containing the acid and the TAA salt discharged from the second dissolution regeneration project can be used as the aqueous acid solution used in the subsequent dissolution regeneration process, whereby the regenerated TAA salt can be obtained without waste.
排出液中是否含酸可以通過測定該排出液的pH、導電率等來掌握。Whether or not the acid is contained in the discharge liquid can be grasped by measuring the pH, conductivity, and the like of the discharge liquid.
圖4中示出排出液的導電率,首先,隨著TMACl的溶出,排出液的導電率上升,隨著排出液中該TMACl的濃度變穩定,排出液的導電率也穩定,此後,一旦HCl流出,則排出液的導電率急劇上升。利用該現象,通過監測排出液的導電率,可以進行從上述第一溶離再生工程到第二溶離再生工程的切換。The conductivity of the discharge liquid is shown in Fig. 4. First, as the TAMCl is eluted, the conductivity of the discharge liquid rises, and as the concentration of the TMACl in the discharge liquid becomes stable, the conductivity of the discharge liquid is also stabilized, and thereafter, once HCl When it flows out, the conductivity of the discharge liquid rises sharply. By using this phenomenon, by monitoring the conductivity of the discharge liquid, switching from the first dissolution regeneration process to the second dissolution regeneration process can be performed.
此時,透過在排出液的切換生產線上設置緩衝罐(未圖示)、或者在距導電計的測量位置足夠下游的位置設置流路切換裝置,可以使第一溶離再生工程的排出液中不含在導電率急劇上升時會含有的HCl(可以獲得不含酸的TAA鹽水溶液。)。At this time, by providing a buffer tank (not shown) on the discharge line of the discharge liquid or providing a flow path switching device at a position sufficiently downstream from the measurement position of the conductivity meter, the discharge liquid of the first dissolution regeneration project can be prevented. It contains HCl which is contained when the conductivity is sharply increased (a TAA salt solution containing no acid can be obtained).
根據上述本發明的TAA鹽水溶液的製造方法,可以獲得高濃度且高純度的TAA鹽水溶液。通過本發明的製造方法獲得的TAA鹽水溶液中的TAA離子濃度還要取決於酸水溶液的濃度、或陽離子交換樹脂的性能,而在使用氫氧化TAA濃度為0.001~1質量%的原料水溶液的情況下,通常可以獲得2~40質量%的TAA鹽水溶液。According to the method for producing a TAA salt aqueous solution of the present invention described above, a TAA salt aqueous solution having a high concentration and a high purity can be obtained. The TAA ion concentration in the TAA salt aqueous solution obtained by the production method of the present invention depends on the concentration of the aqueous acid solution or the performance of the cation exchange resin, and in the case of using an aqueous solution of a raw material having a TAA concentration of 0.001 to 1% by mass. Next, a 2 to 40% by mass aqueous solution of TAA salt can be usually obtained.
另外,所得TAA鹽水溶液可以透過公知的方法製成氫氧化TAA。作為該方法,可列舉出電滲析、電解等。Further, the obtained TAA salt aqueous solution can be made into a TAA hydroxide by a known method. Examples of the method include electrodialysis, electrolysis, and the like.
進而,在供於電滲析、電解之前,還可以進行TAA鹽水溶液的純化、濃縮。作為TAA鹽水溶液的純化方法,可列舉出:使該水溶液與陽離子交換樹脂、和/或螯合樹脂(chelating resin)接觸來除去TAA鹽水溶液中的金屬離子成分的方法;使TAA鹽水溶液與活性炭等吸附劑、或陰離子交換樹脂接觸來除去光致抗蝕劑等有機物的方法等。Further, before the electrodialysis and electrolysis, the TAA salt aqueous solution can be purified and concentrated. The method for purifying the TAA salt aqueous solution may be a method of removing the metal ion component in the TAA salt aqueous solution by contacting the aqueous solution with a cation exchange resin and/or a chelating resin; and making the TAA salt aqueous solution and activated carbon A method in which an adsorbent or an anion exchange resin is contacted to remove an organic substance such as a photoresist.
另外,作為TAA鹽水溶液的濃縮方法,具體來說,可列舉出利用電滲析、蒸發罐、反滲透膜進行濃縮的方法等。In addition, as a method of concentrating the TAA salt aqueous solution, specifically, a method of concentrating by electrodialysis, an evaporation can, or a reverse osmosis membrane may be mentioned.
為了具體說明本發明,以下舉出實施例進行說明,但本發明並不限定於這些例子。In order to specifically describe the present invention, the following examples are described, but the present invention is not limited to these examples.
此外,使用由液晶工廠排放的含有四甲基氫氧化銨(以下,簡稱為TMAH。)的廢液作為試樣液。Further, a waste liquid containing tetramethylammonium hydroxide (hereinafter abbreviated as TMAH) discharged from a liquid crystal factory is used as a sample liquid.
另外,pH通過pH電極法(測定裝置:HM-30R(DKK-TOA CORPORATION製造))來測定並換算而得,TMAC1濃度通過離子色譜法(測定裝置:DX120(Dionex公司))來測定TMA離子濃度並換算而得。對於HCl濃度,通過離子色譜法(測定裝置:DX320(Dionex公司))來測定Cl濃度,並將除與TMA離子配對的Cl離子以外的過量的Cl離子換算成HCl濃度。In addition, the pH was measured and converted by a pH electrode method (measurement apparatus: HM-30R (manufactured by DKK-TOA CORPORATION)), and the TMAC1 concentration was measured by ion chromatography (measurement apparatus: DX120 (Dionex)) to determine the TMA ion concentration. And converted to get. With respect to the HCl concentration, the Cl concentration was measured by ion chromatography (measurement apparatus: DX320 (Dionex)), and excess Cl ions other than Cl ions paired with TMA ions were converted into HCl concentration.
將交換容量4.4mol/L的弱酸性陽離子交換樹脂DIAION WK40L(三菱化學公司製造)1000ml填充到直徑50mm的柱中,使總交換容量為4.4mol、樹脂高度為500mm。1000 ml of a weakly acidic cation exchange resin DIAION WK40L (manufactured by Mitsubishi Chemical Corporation) having an exchange capacity of 4.4 mol/L was packed in a column having a diameter of 50 mm to have a total exchange capacity of 4.4 mol and a resin height of 500 mm.
以SV(空間速度)=100h-1 向上述填充塔中通入BV=2000(L/L-樹脂)的試樣液(TMAH濃度:0.045質量%),進行TMA離子的吸附。A sample liquid (TMAH concentration: 0.045 mass%) of BV = 2000 (L/L-resin) was introduced into the above-mentioned packed column at SV (space velocity) = 100 h -1 to carry out adsorption of TMA ions.
此時,排出液中檢出TMA離子的點為BV=430(L/L-樹脂),穿透容量為2.12mol。此時,穿透點下的交換率為48.2%。接著,使目標吸附率為80%時通液量為BV=1000(L/L-樹脂),此時的處理排水中所含的TMA離子的總量(TMA離子洩漏量)為1.48mol。由此,由式(1)求出的n為2,所需填充塔數確定為2塔。At this time, the point at which the TMA ion was detected in the discharged liquid was BV = 430 (L/L-resin), and the breakthrough capacity was 2.12 mol. At this time, the exchange rate at the breakthrough point was 48.2%. Next, when the target adsorption rate was 80%, the liquid passing amount was BV = 1000 (L/L-resin), and the total amount of TMA ions (TMA ion leakage amount) contained in the treated wastewater at this time was 1.48 mol. Thus, n obtained by the formula (1) is 2, and the number of required packed columns is determined to be 2 columns.
準備與上述填充塔相同的填充塔,串聯設置2塔形成初始填充塔生產線。以上游側為第一填充塔、下游側為第二填充塔。將第一填充塔的目標交換率設定為80%,以BV=1000(L/L-樹脂)向該填充塔生產線中通入0.045質量%的TMAH顯影廢液。此時,來自第二填充塔的排出液中未確認到TMA離子的洩漏。A packed column identical to the above packed column was prepared, and two columns were placed in series to form an initial packed column production line. The upstream side is the first packed column and the downstream side is the second packed column. The target exchange rate of the first packed column was set to 80%, and 0.045% by mass of TMAH developing waste liquid was introduced into the packed column production line at BV = 1000 (L/L-resin). At this time, no leakage of TMA ions was observed in the discharged liquid from the second packed column.
接著,斷開第一填充塔,以SV=3h-1 向第一填充塔中通入作為溶離液的6000ml的1N-HCl,使所吸附的TMA離子以TMAC1的形式溶出。排出液進行分取來分成兩部分液體。將最初的1000ml作為第一分取液。該第一分取液不含TMACl,作為廢液進行處理。接下來的5000ml作為第二分取液。該第二分取液包含7.3質量%(0.67mol/l)的TMACl和0.02質量%(0.01mol/l)的HCl。該第二分取液為所期望的TMACl溶液。Next, the first packed column was opened, and 6000 ml of 1N-HCl as a solution was introduced into the first packed column at SV = 3 h -1 to elute the adsorbed TMA ions as TMAC1. The effluent is fractionated to separate into two parts of the liquid. The first 1000 ml was taken as the first fraction. The first fractionation solution does not contain TCAM1 and is treated as a waste liquid. The next 5000 ml was taken as the second fraction. The second fraction contained 7.3% by mass (0.67 mol/l) of TCAMl and 0.02% by mass (0.01 mol/l) of HCl. The second fraction is the desired TCAMCl solution.
第一填充塔的溶離再生工程結束後,形成上游側為第二填充塔、下游側為第一填充塔的填充塔生產線,使得可以從第二填充塔向第一填充塔通液。以BV=700(L/L-樹脂)通入0.045質量%的TMAH顯影廢液,結果第二填充塔的交換率達到80%。此時,來自第一填充塔的排出液中未確認到TMA離子的洩漏。After the dissolution and regeneration of the first packed column is completed, a packed column production line having a second packed column on the upstream side and a first packed column on the downstream side is formed so that the first packed column can be passed through the second packed column. When 0.045 mass% of TMAH developing waste liquid was passed at BV = 700 (L/L-resin), the exchange rate of the second packed column was 80%. At this time, no leakage of TMA ions was observed in the discharged liquid from the first packed column.
接著,斷開第二填充塔,以SV=3h-1 向第二填充塔中通入作為溶離液的6000ml的1N-HCl,使所吸附的TMA離子以TMACl的形式溶出。排出液進行分取來分成兩部分液體。將最初的1000ml作為第一分取液。該第一分取液不含TMACl,作為廢液進行處理。接下來的5000ml作為第二分取液。該第二分取液含有7.3質量%(0.67mol/l)的TMACl和0.02質量%(0.01mol/l)的HCl。該第二分取液為所期望的TMACl溶液。Next, the second packed column was opened, and 6000 ml of 1N-HCl as a solution was introduced into the second packed column at SV = 3 h -1 to elute the adsorbed TMA ions in the form of TMACl. The effluent is fractionated to separate into two parts of the liquid. The first 1000 ml was taken as the first fraction. The first fractionation solution does not contain TCAM1 and is treated as a waste liquid. The next 5000 ml was taken as the second fraction. The second fraction contained 7.3% by mass (0.67 mol/l) of TMACl and 0.02% by mass (0.01 mol/l) of HCl. The second fraction is the desired TCAMCl solution.
各個填充塔的回收率(%)由“分取液中的TMACl的量(mol)/填充塔中的陽離子交換樹脂所吸附的TMA量(mol)”求出。第一填充塔和第二填充塔均為94.6%。The recovery rate (%) of each packed column was determined from "the amount (mol) of TMACl in the fractionating liquid / the amount of TMA (mol) adsorbed by the cation exchange resin in the packed column". Both the first packed column and the second packed column were 94.6%.
在實施例2~11中,如表1所示使目標交換率分別為50~95,除此之外,與實施例1同樣地進行,算出n,確定填充塔生產線的塔數,通入TMAH試樣液,使TMA離子吸附,製造TMACl。結果示於表1。In the examples 2 to 11, as shown in Table 1, the target exchange rate was changed to 50 to 95, and in the same manner as in the first embodiment, n was calculated, and the number of towers in the packed column production line was determined, and TMAH was introduced. The sample solution adsorbs TMA ions to produce TMACl. The results are shown in Table 1.
在與實施例1同樣的條件下,將目標吸附率設定為45%,以BV=400(L/L-樹脂)通入0.045質量%的TMAH顯影廢液。Under the same conditions as in Example 1, the target adsorption rate was set to 45%, and 0.045% by mass of TMAH developing waste liquid was introduced at BV = 400 (L/L-resin).
以SV=3h-1 向第一填充塔中通入作為溶離液的6000ml的1N-HCl,使所吸附的TMA離子以TMACl的形式溶出。溶出液進行分取來分成兩部分液體。將最初的1000ml作為第一分取液。該第一分取液不含TMACl,作為廢液進行處理。接下來的5000ml作為第二分取液。該第二分取液含有3.4質量%(0.37mol/l)的TMACl和2.21質量%(0.61mol/l)的HCl。6000 ml of 1N-HCl as a solution was introduced into the first packed column at SV = 3 h -1 to elute the adsorbed TMA ions in the form of TMACl. The eluate is fractionated to separate into two parts of the liquid. The first 1000 ml was taken as the first fraction. The first fractionation solution does not contain TCAM1 and is treated as a waste liquid. The next 5000 ml was taken as the second fraction. The second fraction contained 3.4% by mass (0.37 mol/l) of TCAMCl and 2.21% by mass (0.61 mol/l) of HCl.
比較例1為將實施例1的目標吸附率由80%變更為45%的例子,最終獲得的TMACl溶液的濃度低、包含大量的HCl。Comparative Example 1 is an example in which the target adsorption ratio of Example 1 was changed from 80% to 45%, and the concentration of the finally obtained TMACl solution was low and contained a large amount of HCl.
在使用與上述實施例1同樣的填充塔和試樣液、同樣將目標吸附率設定為80%的情況下,所需填充塔數n為2根,為了連續地進行吸附處理,形成由n+1的3塔構成的填充塔生產線。When the packed column and the sample liquid are used in the same manner as in the above-described first embodiment, and the target adsorption rate is set to 80%, the number of required packed columns n is two, and in order to continuously perform the adsorption treatment, n + is formed. A packed tower production line consisting of 1 of 3 towers.
與實施例1同樣,在上游側設置第一填充塔、並在下游側設置第二填充塔,形成填充塔生產線。用串聯設置2塔而成的樹脂塔進行吸附處理。此時,第三填充塔待命。In the same manner as in the first embodiment, a first packed column was provided on the upstream side and a second packed column was provided on the downstream side to form a packed column production line. The adsorption treatment was carried out by using a resin tower in which two columns were connected in series. At this time, the third packed tower is on standby.
第一填充塔的吸附結束後,斷開第一填充塔,以能從第二填充塔向第三填充塔通液的形式串聯設置,形成新的填充塔生產線。以BV=700(L/L-樹脂)向該新的填充塔生產線中通入0.045質量%的TMAH顯影廢液,結果第二填充塔的交換率達到80%。此時,來自第三填充塔的排出液中未確認到TMA離子的洩漏。After the adsorption of the first packed column is completed, the first packed column is disconnected so as to be able to be connected in series from the second packed column to the third packed column to form a new packed column production line. 0.045% by mass of TMAH developing waste liquid was introduced into the new packed column production line at BV = 700 (L/L-resin), and as a result, the exchange rate of the second packed column reached 80%. At this time, no leakage of TMA ions was observed in the discharged liquid from the third packed column.
與上述吸附工程(第二填充塔→第三填充塔)同時進行第一填充塔的溶離再生工程。以SV=3h-1 向第一填充塔中通入作為溶離液的6000ml的1N-HCl,使所吸附的TMA離子以TMACl的形式溶出。溶出液進行分取來分成兩部分液體。將最初的1000ml作為第一分取液。該第一分取液不含TMACl,作為廢液進行處理。接下來的5000ml作為第二分取液。該第二分取液含有7.3質量%(0.67mol/l)的TMACl和0.02質量%(0.01mol/l)的HCl。該第二分取液為所期望的TMACl溶液。The dissolution and regeneration of the first packed column is performed simultaneously with the above adsorption process (second packed column → third packed column). 6000 ml of 1N-HCl as a solution was introduced into the first packed column at SV = 3 h -1 to elute the adsorbed TMA ions in the form of TMACl. The eluate is fractionated to separate into two parts of the liquid. The first 1000 ml was taken as the first fraction. The first fractionation solution does not contain TCAM1 and is treated as a waste liquid. The next 5000 ml was taken as the second fraction. The second fraction contained 7.3% by mass (0.67 mol/l) of TMACl and 0.02% by mass (0.01 mol/l) of HCl. The second fraction is the desired TCAMCl solution.
在本實施例中,第一填充塔的溶離再生工程在上述吸附工程(第二填充塔→第三填充塔)中的第二填充塔達到目標交換率之前結束。因此,可以的是,在第二填充塔達到目標交換率、吸附工程(第二填充塔→第三填充塔)結束後立刻將得到再生的第一填充塔連接到第三填充塔的下游側,形成新的填充塔生產線(第三填充塔→第一填充塔),立即進行使用該填充塔生產線(第三填充塔→第一填充塔)的吸附工程,並且同時進行達到了目標交換率的第二填充塔的溶離再生工程,可以連續地進行TMACl溶液的製造。In the present embodiment, the dissolution regeneration process of the first packed column ends before the second packed column in the adsorption process (second packed column → third packed column) reaches the target exchange rate. Therefore, it is possible to connect the regenerated first packed column to the downstream side of the third packed column immediately after the second packed column reaches the target exchange rate and the adsorption process (second packed column → third packed column) ends. Forming a new packed tower production line (third packed tower → first packed tower), immediately performing adsorption engineering using the packed tower production line (third packed tower → first packed tower), and simultaneously achieving the target exchange rate In the dissolution regeneration process of the two packed columns, the production of the TMACl solution can be continuously performed.
圖1為表示本發明的TAA鹽水溶液的製造方法的概要的框圖。Fig. 1 is a block diagram showing an outline of a method for producing a TAA salt aqueous solution of the present invention.
圖2為表示本發明的TAA鹽水溶液的製造方法的優選方式的流程圖。Fig. 2 is a flow chart showing a preferred embodiment of the method for producing a TAA salt aqueous solution of the present invention.
圖3為表示本發明的TAA鹽水溶液的製造方法的另一優選方式的流程圖。Fig. 3 is a flow chart showing another preferred embodiment of the method for producing a TAA salt aqueous solution of the present invention.
圖4為表示排出液中的TAA鹽(TMACl)和氯化氫(HCl)的濃度、以及排出液的導電率的圖表。4 is a graph showing the concentration of TAA salt (TMACl) and hydrogen chloride (HCl) in the discharge liquid, and the conductivity of the discharge liquid.
Claims (7)
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2010174214A JP5717997B2 (en) | 2010-08-03 | 2010-08-03 | Method for producing aqueous tetraalkylammonium salt solution |
Publications (2)
Publication Number | Publication Date |
---|---|
TW201208766A TW201208766A (en) | 2012-03-01 |
TWI485003B true TWI485003B (en) | 2015-05-21 |
Family
ID=45844286
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
TW100127414A TWI485003B (en) | 2010-08-03 | 2011-08-02 | Method for producing tetraalkylammonium salt solution |
Country Status (4)
Country | Link |
---|---|
JP (1) | JP5717997B2 (en) |
KR (1) | KR101806823B1 (en) |
CN (1) | CN102407171B (en) |
TW (1) | TWI485003B (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
TWI715507B (en) * | 2020-06-12 | 2021-01-01 | 國立清華大學 | Processing method for wastewater containing tetramethylammonium chloride and processing device for wastewater containing tetramethylammonium chloride |
TWI842314B (en) * | 2022-12-30 | 2024-05-11 | 三福化工股份有限公司 | Method and device for reclaim tetramethylammonium hydroxide in the developing waste liquid and removal of nitrogen-containing compounds |
Families Citing this family (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP6387637B2 (en) * | 2014-03-18 | 2018-09-12 | 栗田工業株式会社 | Ion exchange apparatus and ion exchange treatment method |
CN104974048A (en) * | 2014-04-11 | 2015-10-14 | 湖州欧美新材料有限公司 | High-purity tetraalkylammonium chloride water solution, preparation method and application thereof |
CN105294455B (en) * | 2015-10-09 | 2017-10-27 | 南京工业大学 | Method for preparing tetrabutyl ammonium hydroxide aqueous solution by anion exchange |
JP7124508B2 (en) * | 2018-07-18 | 2022-08-24 | 住友金属鉱山株式会社 | Lithium adsorption method |
CN109802643B (en) * | 2018-11-30 | 2020-09-08 | 无锡市好达电子股份有限公司 | Auxiliary development layout manufacturing method |
CN113200869B (en) * | 2021-04-28 | 2023-06-23 | 南京长江江宇环保科技股份有限公司 | Method for recycling tetramethyl ammonium chloride from semiconductor development wastewater |
Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2000288538A (en) * | 1999-04-07 | 2000-10-17 | Japan Organo Co Ltd | Treating method for nitrogen-containing wastewater |
JP2004066102A (en) * | 2002-08-06 | 2004-03-04 | Babcock Hitachi Kk | Waste liquid treatment method and equipment therefor |
JP2009142764A (en) * | 2007-12-14 | 2009-07-02 | Japan Organo Co Ltd | Method and apparatus for recovering iodine from iodine-containing waste liquid |
Family Cites Families (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US4522726A (en) * | 1984-07-30 | 1985-06-11 | Progress Equities Incorporated | Advanced separation device and method |
IL89607A0 (en) * | 1988-03-31 | 1989-09-10 | Reo Lp | Process for fractionating a mixture of rare earth metals by ion exchange |
KR100264643B1 (en) * | 1992-11-10 | 2000-09-01 | 쓰라히데 죠오 | Method of processing organic quaternary ammonium hydroxide-containing waste liquid |
JP2730610B2 (en) * | 1992-11-10 | 1998-03-25 | 多摩化学工業株式会社 | Method for treating wastewater containing organic quaternary ammonium hydroxide |
JP3200301B2 (en) * | 1994-07-22 | 2001-08-20 | オルガノ株式会社 | Method and apparatus for producing pure or ultrapure water |
JPH09225324A (en) * | 1996-02-22 | 1997-09-02 | Japan Organo Co Ltd | Regeneration of ion exchange resin or synthetic adsorbing material for removing organic impurities |
JP3903831B2 (en) * | 2002-04-10 | 2007-04-11 | 栗田工業株式会社 | Boric acid analysis method and analyzer, ultrapure water production method and production apparatus |
-
2010
- 2010-08-03 JP JP2010174214A patent/JP5717997B2/en active Active
-
2011
- 2011-07-22 KR KR1020110072968A patent/KR101806823B1/en active IP Right Grant
- 2011-08-02 TW TW100127414A patent/TWI485003B/en active
- 2011-08-03 CN CN201110221353.0A patent/CN102407171B/en active Active
Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2000288538A (en) * | 1999-04-07 | 2000-10-17 | Japan Organo Co Ltd | Treating method for nitrogen-containing wastewater |
JP2004066102A (en) * | 2002-08-06 | 2004-03-04 | Babcock Hitachi Kk | Waste liquid treatment method and equipment therefor |
JP2009142764A (en) * | 2007-12-14 | 2009-07-02 | Japan Organo Co Ltd | Method and apparatus for recovering iodine from iodine-containing waste liquid |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
TWI715507B (en) * | 2020-06-12 | 2021-01-01 | 國立清華大學 | Processing method for wastewater containing tetramethylammonium chloride and processing device for wastewater containing tetramethylammonium chloride |
TWI842314B (en) * | 2022-12-30 | 2024-05-11 | 三福化工股份有限公司 | Method and device for reclaim tetramethylammonium hydroxide in the developing waste liquid and removal of nitrogen-containing compounds |
Also Published As
Publication number | Publication date |
---|---|
CN102407171A (en) | 2012-04-11 |
JP2012030208A (en) | 2012-02-16 |
KR20120022567A (en) | 2012-03-12 |
KR101806823B1 (en) | 2017-12-08 |
CN102407171B (en) | 2015-07-29 |
TW201208766A (en) | 2012-03-01 |
JP5717997B2 (en) | 2015-05-13 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
TWI485003B (en) | Method for producing tetraalkylammonium salt solution | |
TWI495509B (en) | Method for preparing tetraalkylammonium salts and preparing tetraalkylammonium hydroxide using the same | |
WO2011036942A1 (en) | Process for production of tetraalkylammonium hydroxide | |
JP2007181833A (en) | Method for treating tetraalkylammonium ion-containing solution | |
JP5808221B2 (en) | Method for producing tetraalkylammonium salt solution | |
TWI583658B (en) | Method for producing high-concentration solution of tetraalkylammonium salt | |
JP5167253B2 (en) | Processing method of developing waste liquid containing tetraalkylammonium ions | |
JP2730610B2 (en) | Method for treating wastewater containing organic quaternary ammonium hydroxide | |
WO2015016230A1 (en) | Preparation method of aqueous tetraalkyl ammonium salt solution | |
JP2013119487A (en) | Method for treating hydrosilicofluoric acid-containing liquid | |
TWI732106B (en) | Method for treating tetrafluoroborate-containing wastewater | |
TWI423836B (en) | Process for recovering and purifying tetraalkyl ammonium hydroxide from waste solution containing the same | |
JP6387637B2 (en) | Ion exchange apparatus and ion exchange treatment method | |
WO2011074495A1 (en) | Method for reusing waste liquid from which tetraalkylammonium ions have been removed | |
JP7477641B2 (en) | Method and apparatus for purifying liquid containing tetraalkylammonium ions | |
JP7456027B1 (en) | Method and apparatus for recovering tetramethylammonium hydroxide from developer waste solution and removing nitrogen-containing compounds | |
JP2004275948A (en) | Boron removal process and boron removal apparatus | |
JP2002233773A (en) | Method for recovering water containing high purity boron and device for treating boron eluting solution eluted from resin selectively adsorbing boron |