TWI532681B - A method for recovering ethylene glycol and acetaldehyde from polyester wastewater - Google Patents

A method for recovering ethylene glycol and acetaldehyde from polyester wastewater Download PDF

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TWI532681B
TWI532681B TW102145666A TW102145666A TWI532681B TW I532681 B TWI532681 B TW I532681B TW 102145666 A TW102145666 A TW 102145666A TW 102145666 A TW102145666 A TW 102145666A TW I532681 B TWI532681 B TW I532681B
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acetaldehyde
ethylene glycol
column
wastewater
tower
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TW201434758A (en
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shao-peng Wang
Xue-Bin Zhang
Ding Bai
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    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
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    • Y02P20/52Improvements relating to the production of bulk chemicals using catalysts, e.g. selective catalysts

Description

一種聚酯廢水中回收乙二醇和乙醛的方法 Method for recovering ethylene glycol and acetaldehyde in polyester wastewater

本發明係有關一種化工過程中,聚酯廢水中有機物的回收與再利用的方法,特別涉及一種聚酯廢水中回收乙二醇和乙醛的方法。 The invention relates to a method for recovering and reusing organic matter in polyester wastewater in a chemical process, in particular to a method for recovering ethylene glycol and acetaldehyde in polyester wastewater.

在聚酯產業快速發展同時,大量的工業廢水也隨之產生,尤其是在重要的酯化反應過程中會產生大量的酯化廢水,而由於這些酯化廢水中含有乙醛、乙二醇、2-甲基-1,3-二氧環戊烷等有機物(其中易揮發組分乙醛占總有機污染物的50%左右),廢水的COD(化學需氧量)濃度高達20000-30000mg/L,這不僅增加了廢水的下游處理成本,同時也加劇了聚酯工業發展中所面臨的資源、環境與效益之間矛盾激化。 At the same time as the rapid development of the polyester industry, a large amount of industrial wastewater is also produced, especially in the process of important esterification, a large amount of esterification wastewater is produced, and since these esterification wastewaters contain acetaldehyde and ethylene glycol, Organic substances such as 2-methyl-1,3-dioxocyclopentane (where the volatile component acetaldehyde accounts for about 50% of the total organic pollutants), and the COD (chemical oxygen demand) concentration of the wastewater is as high as 20000-30000 mg/ L, this not only increases the downstream treatment cost of wastewater, but also exacerbates the conflict between the resources, environment and benefits faced in the development of the polyester industry.

目前,國內外對酯化廢水的處理主要採用以下幾種方式進行。 At present, the treatment of esterification wastewater at home and abroad is mainly carried out in the following ways.

厭氧-好氧法處理該廢水。但由於醛類物質毒性非常大,不利於細菌生長,導致生化方法處理效率較低,而且對於如此高COD值的廢水,單獨採用生物法處理不但投資費用高而且處理成本也很昂貴,企業負擔重。 The wastewater is treated by an anaerobic-aerobic process. However, due to the very high toxicity of aldehydes, it is not conducive to bacterial growth, resulting in low biochemical treatment efficiency. For such high COD wastewater, biological treatment alone is not only expensive but also expensive to process. .

汽提後再焚燒的方法處理該廢水。汽提後,COD值降到5000mg/L以下,然後將塔頂物料通入熱煤爐進行焚燒,並綜合利用其熱能,但是焚燒生成的二氧化碳造成溫室效應,燃燒不完全還會產生二次汙染,而且焚燒要求安全係數相當高否則易發生爆炸,整體上來說焚燒。這些有價值的有機物不是最經濟的方式。 The wastewater is treated by steaming and then incinerating. After stripping, the COD value drops below 5000mg/L, and then the top material is introduced into the hot coal furnace for incineration, and the heat energy is comprehensively utilized, but the carbon dioxide generated by incineration causes a greenhouse effect, and incomplete combustion will also cause secondary pollution. And the incineration requires a high safety factor or it is prone to explosion and burns as a whole. These valuable organics are not the most economical way.

約翰.布朗德國工程有限公司採用連續減壓蒸餾,如中國專利號(CN16854A),從而得到純度很高的乙二醇,該方法費用較高,且能耗較大。 John. Brown German Engineering Co., Ltd. uses continuous vacuum distillation, such as the Chinese patent number (CN16854A), to obtain high purity ethylene glycol, which is costly and consumes a lot of energy.

反滲透膜的方法,如中國專利號(CN1301238C)回收酯化廢 水中乙二醇,該方法得到乙二醇的純度較高但是不能將乙醛分離出來尤其是採用的反滲透膜都是從國外進口的,技術依賴性大,成本高。而且上述方法沒有考慮到乙醛的回收,尤其是含量較大的副產物2-甲基-1,3-二氧戊環的對水污染或COD值的影響等問題。 Reverse osmosis membrane method, such as Chinese patent number (CN1301238C) recycling esterification waste Ethylene glycol in water, the method obtains high purity of ethylene glycol but can not separate acetaldehyde, especially the reverse osmosis membrane is imported from abroad, with high technical dependence and high cost. Moreover, the above method does not take into account the recovery of acetaldehyde, especially the influence of the relatively large amount of by-product 2-methyl-1,3-dioxolane on water pollution or COD value.

近來,如中國專利號(CN1974508A)報導了汽提後通過催化離子交換來間歇處理2-甲基-1,3-二氧戊環副產物然後再分別處理回收乙醛和乙二醇等技術回收酯化廢水中乙二醇和乙醛的方法。該方法能夠得到純度很高的乙二醇,但是採用了水直接吸收乙醛蒸汽,造成工業用水加大而且得到的乙醛溶液濃度太低,需要後續處理,增加了處理成本,而且該方法是間歇的方法,尤其是引入了間歇酸催化處理副產物2-甲基-1,3-二氧戊環,由於酸的腐蝕性,這樣對工業化設備要求很高,而且由於2-甲基-1,3-二氧戊環生成乙醛和乙二醇是一個可逆反應,在間歇處理完後,進去下一道工序難保乙醛和乙二醇不會再生成2-甲基-1,3-二氧戊環。 Recently, as reported in the Chinese Patent No. (CN1974508A), the 2-methyl-1,3-dioxolane by-product was intermittently treated by catalytic ion exchange after stripping, and then the recovery of acetaldehyde and ethylene glycol was separately processed. A method of esterifying ethylene glycol and acetaldehyde in wastewater. The method can obtain ethylene glycol with high purity, but uses water to directly absorb acetaldehyde vapor, which causes industrial water to increase and the concentration of the obtained acetaldehyde solution is too low, which requires subsequent treatment, which increases the processing cost, and the method is The batch process, especially the introduction of the 2-methyl-1,3-dioxolane by-product of the intermittent acid catalysis, is highly demanding for industrial equipment due to the corrosive nature of the acid, and due to the 2-methyl-1 The formation of acetaldehyde and ethylene glycol by 3-dioxolane is a reversible reaction. After the batch treatment, it is difficult to ensure that acetaldehyde and ethylene glycol will not form 2-methyl-1,3-di in the next step. Oxolane.

基於解決以上所述習知技藝的缺失,本發明為一種聚酯廢水中回收乙二醇和乙醛的方法,其主要目的在於化工過程中,聚酯廢水中有機物的回收與再利用的方法,特別涉及一種聚酯廢水中回收乙二醇和乙醛的方法。 Based on the solution to the above-mentioned shortcomings of the prior art, the present invention is a method for recovering ethylene glycol and acetaldehyde in polyester wastewater, the main purpose of which is to recover and reuse organic matter in polyester wastewater in a chemical process, in particular A method for recovering ethylene glycol and acetaldehyde in a polyester wastewater.

本發明同時收到了良好的經濟效益和節能降耗的目的: The invention also receives good economic benefits and the purpose of energy saving and consumption reduction:

(1)本發明能夠得到純度超過95%的乙二醇溶液和大於98%的乙醛產品。 (1) The present invention is capable of obtaining an ethylene glycol solution having a purity of more than 95% and an acetaldehyde product of more than 98%.

(2)大大降低了處理後酯化廢水的COD值,使COD值從不小於20000mg/L降到3000mg/L以下,實現達標排放。 (2) The COD value of the treated esterification wastewater is greatly reduced, and the COD value is reduced from not less than 20,000 mg/L to less than 3000 mg/L, and the discharge is achieved.

(3)簡化了乙醛和乙二醇回收技術流程,充分利用原有單元設施進行乙二醇回收,省去了新裝置的投入消耗和控制系統,並將回收得到的乙二醇直接進入酯化反應釜,繼續進行酯化反應,省卻了將乙二醇收集、純化,制漿後再投入反應的步驟,從而使酯化反應和廢水處理回收實現了連續迴圈運行,真正實現節能降耗。 (3) Simplified the technical process of acetaldehyde and ethylene glycol recovery, making full use of the original unit facilities for ethylene glycol recovery, eliminating the input and consumption and control system of the new device, and directly recovering the recovered ethylene glycol into the ester. The reaction kettle continues the esterification reaction, eliminating the steps of collecting, purifying, and then converting the ethylene glycol into a reaction, thereby realizing the continuous loop operation of the esterification reaction and the wastewater treatment and recycling, realizing energy saving and consumption reduction. .

綜上可知,本發明不僅能夠得到高純度的乙二醇和乙醛產品,而且減少了後續的處理技術,具有良好的經濟和環境效益。同時技術流程的改進也為行業內乙醛和乙二醇的回收工作在節能降耗方面做出了表率。 In summary, the present invention not only can obtain high-purity ethylene glycol and acetaldehyde products, but also reduces subsequent processing techniques, and has good economic and environmental benefits. At the same time, the improvement of technical process has also set an example for the recovery of acetaldehyde and ethylene glycol in the industry in terms of energy saving.

1‧‧‧氣提塔 1‧‧‧Flat Tower

101‧‧‧蒸汽 101‧‧‧Steam

2‧‧‧乙醛精餾塔 2‧‧‧acetaldehyde distillation tower

201‧‧‧蒸汽 201‧‧‧Steam

202‧‧‧廢水收集裝置 202‧‧‧Waste collection device

203‧‧‧蒸汽回收裝置 203‧‧‧Steam recovery unit

3‧‧‧乙二醇蒸餾塔 3‧‧‧ glycol distillation tower

301‧‧‧乙二醇加熱裝置 301‧‧‧Glycol heating device

302‧‧‧蒸汽回收裝置 302‧‧‧Steam recovery unit

圖1是改進前處理技術流程圖;圖2是改進後的處理技術流程圖。 1 is a flow chart of an improved pre-processing technique; and FIG. 2 is a flow chart of an improved processing technique.

茲配合下列之圖式說明本發明之詳細結構,及其連結關係,以利於 貴審委做一瞭解。 The detailed structure of the present invention and its connection relationship will be described in conjunction with the following drawings to facilitate an understanding of the audit committee.

為實現高純度的乙醛及乙二醇回收,並進一步降低裝置運行能耗,本發明在前期申請,如中國專利申請號(201010602167.7)的基礎上再進行大膽改進,進一步簡化了技術流程,達到了節能降耗的目的。 In order to achieve high purity acetaldehyde and ethylene glycol recovery, and further reduce the energy consumption of the device operation, the present invention further simplifies the technical process by further making bold improvements on the basis of the prior application, such as the Chinese patent application number (201010602167.7). The purpose of energy saving and consumption reduction.

本發明提供的一種聚酯廢水中回收乙二醇和乙醛的方法,其中乙二醇的回收是依據2-甲基-1,3-二氧戊環的分解原理進行回收。在處理廢水過程中不斷采出並回收高濃度乙醛和乙二醇,使2-甲基-1,3-二氧戊環在高溫條件下的水解不斷向正反應方向進行,最終水解完全。分解原理如下: The invention provides a method for recovering ethylene glycol and acetaldehyde in a polyester wastewater, wherein the recovery of ethylene glycol is recovered according to the decomposition principle of 2-methyl-1,3-dioxolane. During the treatment of wastewater, high concentrations of acetaldehyde and ethylene glycol are continuously recovered and recovered, so that the hydrolysis of 2-methyl-1,3-dioxolane under high temperature conditions proceeds to the positive reaction direction, and the final hydrolysis is complete. The decomposition principle is as follows:

本發明是通過以下的技術方案實現的:一種聚酯廢水中回收乙二醇和乙醛的方法,是一個連續收集的過程,是通過以下的步驟實現的:(1)從酯化單元乙二醇分離塔出來的酯化廢水和蒸汽進入氣提塔處理,在塔頂收集到的有機物氣體與水蒸氣進入乙醛精餾塔;(2)經乙醛精餾塔處理後,在塔頂收集到高純度乙醛,塔底廢水則直接通過回流或單獨走線再進入酯化單元的乙二醇分離塔, 在分離塔內完成乙二醇和水及其他有機物的分離,回收得到的乙二醇直接進入酯化反應釜,繼續進行酯化反應;(3)從酯化分離塔頂出來的收集了有機物的酯化廢水或蒸汽,再次進入氣提塔迴圈處理。 The present invention is achieved by the following technical solution: a method for recovering ethylene glycol and acetaldehyde in polyester wastewater, which is a continuous collection process, which is achieved by the following steps: (1) Ethylene glycol from esterification unit The esterification wastewater and steam from the separation tower are processed into the stripping tower, and the organic gas and water vapor collected at the top of the tower enter the acetaldehyde rectification tower; (2) after being treated by the acetaldehyde rectification tower, collected at the top of the tower. High-purity acetaldehyde, the bottom wastewater is directly passed through the reflux or separate traces to the glycol separation column of the esterification unit. Separation of ethylene glycol and water and other organic substances in the separation column, the recovered ethylene glycol directly enters the esterification reactor to continue the esterification reaction; (3) the organic ester-derived ester from the top of the esterification separation column The wastewater or steam is recycled to the stripping tower for treatment.

所述步驟(1)中的氣提塔需要添加熱傳質,優選熱源為水蒸氣,壓力為0.1-1.0MPa,塔頂壓力為0.1-1.0MPa,塔頂溫度為60-140℃;塔底溫度為80-160℃。 The stripping tower in the step (1) needs to add heat mass transfer, preferably the heat source is water vapor, the pressure is 0.1-1.0 MPa, the top pressure is 0.1-1.0 MPa, the top temperature is 60-140 ° C; The temperature is 80-160 °C.

所述步驟(1)中的酯化廢水包含了原有酯化水和新增有機組分含量的混合水,其COD不小於20000mg/L;所述在塔底收集到的氣提廢水是COD值小於3000mg/L的廢水。在經過氣提塔處理之後的廢水,COD值小於3000mg/L,已經可以直接進行汙水處理。 The esterification wastewater in the step (1) comprises mixed water of the original esterified water and the newly added organic component, and the COD thereof is not less than 20,000 mg/L; the stripping wastewater collected at the bottom of the tower is COD. Waste water with a value of less than 3000 mg/L. After the wastewater treated by the stripping tower, the COD value is less than 3000 mg/L, and the sewage treatment can be directly performed.

步驟(1)中所述的在塔頂收集到的有機物氣體經冷凝後以液體方式用泵打進乙醛精餾塔,或者不經冷凝直接進入乙醛精餾塔。 The organic gas collected at the top of the column described in the step (1) is condensed and pumped into the acetaldehyde rectification column in a liquid manner or directly into the acetaldehyde rectification column without condensation.

步驟(2)中所述的乙醛精餾塔需要添加傳質,優選熱源為水蒸氣,壓力為0.1-1.0MPa,塔頂壓力為0.1-1.0MPa,塔頂溫度為20-80℃,塔底溫度為80-160℃,回流比為0.1-50,操作壓力為0-1.0MPa。 The acetaldehyde rectification column described in the step (2) needs to be added with mass transfer, preferably the heat source is water vapor, the pressure is 0.1-1.0 MPa, the top pressure is 0.1-1.0 MPa, and the temperature at the top of the column is 20-80 ° C, the tower The bottom temperature is 80-160 ° C, the reflux ratio is 0.1-50, and the operating pressure is 0-1.0 MPa.

步驟(2)中所述的乙醛精餾塔在塔頂收集的乙醛純度大於98%。 The acetaldehyde rectification column described in the step (2) has a purity of acetaldehyde collected at the top of the column of more than 98%.

步驟(2)中所述的乙醛精餾塔塔底廢水通過乙二醇分離塔的回流或另外通過管道進入乙二醇分離塔,無需新建乙二醇回收裝置。乙醛精餾塔塔底廢水通過管道進入分離塔塔體的位置位於第1-12塊塔板之間,優選的為第4-8塊塔板之間。 The bottom wastewater of the acetaldehyde rectification column described in the step (2) is returned to the ethylene glycol separation tower through the reflux of the ethylene glycol separation column or additionally through the pipeline, and no new ethylene glycol recovery device is required. The bottom of the acetaldehyde rectification column bottom water is passed between the columns 1 to 12, preferably between the 4th to 8th trays.

優選的,為了保證回收乙二醇的品質,乙醛精餾塔塔底廢水量與分離塔原回流量之比不超過1。 Preferably, in order to ensure the quality of the recovered ethylene glycol, the ratio of the amount of waste water in the bottom of the acetaldehyde distillation column to the original reflux flow rate of the separation column does not exceed one.

所述步驟(2)中在原有酯化單元的乙二醇分離塔塔底收集的乙二醇純度大於95%。 The purity of the ethylene glycol collected in the bottom of the ethylene glycol separation column of the original esterification unit in the step (2) is greater than 95%.

所述步驟(2)中的乙醛精餾塔塔底廢水中含有少量未分解的2-甲基-1,3-二氧戊環和乙醛蒸汽重新進入酯化單元乙二醇分離塔、氣提塔、乙醛精餾塔進行迴圈分解並進一步處理。 The bottom wastewater of the acetaldehyde rectification column in the step (2) contains a small amount of undecomposed 2-methyl-1,3-dioxolane and acetaldehyde vapor and re-enters the esterification unit ethylene glycol separation column. The stripper and the acetaldehyde rectification column are subjected to loop decomposition and further processing.

所述步驟(3)中的從乙二醇分離塔出來的酯化廢水或蒸汽再次進入氣提塔處理,形成一個迴圈回路。 The esterification wastewater or steam from the ethylene glycol separation column in the step (3) is again introduced into the stripping column to form a loop circuit.

乙二醇的回收基於2-甲基-1,3-二氧戊環在加熱的條件下水解為乙醛和乙二醇的可逆反應原理,酯化廢水在通過所述溫度的氣提塔、乙醛精餾塔和乙二醇分離塔過程中,2-甲基-1,3-二氧戊環不斷水解,並且分別在乙醛精餾塔和乙二醇分離塔連續收集乙醛蒸汽和乙二醇溶液,使水解反應連續不斷向正反應方向進行。 The recovery of ethylene glycol is based on the principle of reversible reaction of 2-methyl-1,3-dioxolane to acetaldehyde and ethylene glycol under heating conditions, and the esterification wastewater is passed through a stripping column at the temperature. During the acetaldehyde rectification column and the ethylene glycol separation column, 2-methyl-1,3-dioxolane is continuously hydrolyzed, and acetaldehyde vapor is continuously collected in the acetaldehyde rectification column and the ethylene glycol separation column, respectively. The ethylene glycol solution continuously causes the hydrolysis reaction to proceed to the positive reaction direction.

實施例1 Example 1

(1)從酯化單元乙二醇分離塔出來的酯化廢水(COD值為20000mg/L)和蒸汽進入氣提塔處理,氣提塔的熱傳質為水蒸氣,壓力為0.1MPa,塔頂壓力為0.1MPa,塔頂溫度為60℃;塔底溫度為80℃,在塔頂收集到的有機物氣體與水蒸氣進入乙醛精餾塔,在氣提塔塔底收集的廢水COD值為2655mg/L; (2)乙醛精餾塔的熱源為水蒸氣,壓力為0.1MPa,塔頂壓力為0.1MPa,塔頂溫度為20℃,塔底溫度為80℃,回流比為0.1,操作壓力為0.1MPa。經乙醛精餾塔處理後,在塔頂收集到高純度乙醛,塔底廢水則直接通過回流進入酯化單元的乙二醇分離塔,乙醛精餾塔塔底廢水量與分離塔原回流量之比為1;在分離塔內完成乙二醇和水及其他有機物的分離,回收得到的乙二醇直接進入酯化反應釜,繼續進行酯化反應; (3)從酯化分離塔頂出來的收集了有機物的酯化廢水或蒸汽,再次進入氣提塔迴圈處理。 (1) The esterification wastewater (COD value: 20000 mg/L) from the esterification unit ethylene glycol separation tower and steam are treated in the stripping tower. The heat transfer mass of the stripping tower is water vapor, and the pressure is 0.1 MPa. The top pressure is 0.1 MPa, the temperature at the top of the column is 60 ° C; the temperature at the bottom of the column is 80 ° C. The organic matter gas and water vapor collected at the top of the column enter the acetaldehyde rectification column, and the COD value of the wastewater collected at the bottom of the stripping tower is 2655mg/L; (2) The heat source of the acetaldehyde rectification column is water vapor, the pressure is 0.1 MPa, the pressure at the top of the column is 0.1 MPa, the temperature at the top of the column is 20 ° C, the temperature at the bottom of the column is 80 ° C, the reflux ratio is 0.1, and the operating pressure is 0.1 MPa. . After being treated by the acetaldehyde rectification column, high-purity acetaldehyde is collected at the top of the column, and the bottom wastewater is directly passed through the ethylene glycol separation tower which is refluxed into the esterification unit, and the amount of waste water in the bottom of the acetaldehyde distillation column and the original column of the separation tower The ratio of the flow rate is 1; the separation of ethylene glycol and water and other organic substances is completed in the separation tower, and the recovered ethylene glycol directly enters the esterification reaction kettle to continue the esterification reaction; (3) The esterified wastewater or steam from which the organic matter is collected from the top of the esterification separation column, and again enters the stripping column for treatment.

經本發明提供的技術流程裝置進行處理得到各產物組分及其含量,如表1所示。 The product components and their contents were obtained by the technical flow device provided by the present invention, as shown in Table 1.

實施例2 Example 2

(1)從酯化單元乙二醇分離塔出來的酯化廢水(COD為30000mg/L)和蒸汽進入氣提塔處理,氣提塔的熱傳質為水蒸氣,壓力為1MPa,塔頂壓力為1MPa,塔頂溫度為140℃;塔底溫度為160℃,在塔頂收集到的有機物氣體與水蒸氣進入乙醛精餾塔,在氣提塔塔底收集的廢水COD值為2875mg/L; (2)乙醛精餾塔的熱源為水蒸氣,壓力為1MPa,塔頂壓力為1MPa,塔頂溫度為80℃,塔底溫度為160℃,回流比為50,操作壓力為1MPa。經乙醛精餾塔處理後,在塔頂收集到高純度乙醛,塔底廢水則直接通過另外單獨走線進入酯化單元的乙二醇分離塔,該線路進入分離塔塔體的位置位於第1塊塔板;乙醛精餾塔塔底廢水量與分離塔原回流量之比為0.5;在分離塔內完成乙二醇和水及其他有機物的分離,回收得到的乙二醇直接進入酯化反應釜,繼續進行酯化反應; (3)從酯化分離塔頂出來的收集了有機物的酯化廢水或蒸汽,再次進入氣提塔迴圈處理。 (1) The esterification wastewater (COD is 30,000 mg/L) from the esterification unit ethylene glycol separation tower and steam are treated in the stripping tower. The heat transfer mass of the stripping tower is water vapor, the pressure is 1 MPa, and the pressure at the top of the tower is It is 1 MPa, the temperature at the top of the tower is 140 ° C; the temperature at the bottom of the column is 160 ° C. The organic matter gas and water vapor collected at the top of the tower enter the acetaldehyde rectification tower, and the COD value of the wastewater collected at the bottom of the stripping tower is 2875 mg/L. ; (2) The heat source of the acetaldehyde rectification column is water vapor, the pressure is 1 MPa, the pressure at the top of the column is 1 MPa, the temperature at the top of the column is 80 ° C, the temperature at the bottom of the column is 160 ° C, the reflux ratio is 50, and the operating pressure is 1 MPa. After being treated by the acetaldehyde rectification column, high-purity acetaldehyde is collected at the top of the column, and the bottom wastewater is directly passed through another separate line to enter the ethylene glycol separation tower of the esterification unit, and the line enters the separation tower body at a position The first tray; the ratio of the amount of wastewater at the bottom of the acetaldehyde distillation column to the original reflux of the separation column is 0.5; the separation of ethylene glycol and water and other organic substances is completed in the separation column, and the recovered ethylene glycol directly enters the esterification. The reaction kettle continues the esterification reaction; (3) The esterified wastewater or steam from which the organic matter is collected from the top of the esterification separation column, and again enters the stripping column for treatment.

經本發明提供的技術流程裝置進行處理得到各產物組分及其含量,如表2所示。 The product components and their contents were obtained by the technical flow device provided by the present invention, as shown in Table 2.

實施例3 Example 3

(1)從酯化單元乙二醇分離塔出來的酯化廢水(COD為25000mg/L)和蒸汽進入氣提塔處理,氣提塔的熱傳質為水蒸氣, 壓力為0.6MPa,塔頂壓力為0.5MPa,塔頂溫度為100℃;塔底溫度為120℃,在塔頂收集到的有機物氣體與水蒸氣進入乙醛精餾塔,在氣提塔塔底收集的廢水COD值為2595mg/L; (2)乙醛精餾塔的熱源為水蒸氣,壓力為0.6MPa,塔頂壓力為0.6MPa,塔頂溫度為100℃,塔底溫度為120℃,回流比為4,操作壓力為0.5MPa。經乙醛精餾塔處理後,在塔頂收集到高純度乙醛,塔底廢水則直接通過另外單獨走線進入酯化單元的乙二醇分離塔,該線路進入分離塔塔體的位置位於第12塊塔板;乙醛精餾塔塔底廢水量與分離塔原回流量之比為0.6;在分離塔內完成乙二醇和水及其他有機物的分離,回收得到的乙二醇直接進入酯化反應釜,繼續進行酯化反應; (3)從酯化分離塔頂出來的收集了有機物的酯化廢水或蒸汽,再次進入氣提塔迴圈處理。 (1) The esterification wastewater (COD is 25000 mg/L) from the esterification unit ethylene glycol separation tower and steam are treated in the stripping tower, and the heat transfer mass of the stripping tower is water vapor. The pressure is 0.6MPa, the top pressure is 0.5MPa, the temperature at the top of the tower is 100°C, the temperature at the bottom of the column is 120°C, and the organic gas and water vapor collected at the top of the tower enter the acetaldehyde rectification tower at the bottom of the stripping tower. The collected wastewater has a COD value of 2595 mg/L; (2) The heat source of the acetaldehyde rectification column is water vapor, the pressure is 0.6 MPa, the pressure at the top of the column is 0.6 MPa, the temperature at the top of the column is 100 ° C, the temperature at the bottom of the column is 120 ° C, the reflux ratio is 4, and the operating pressure is 0.5 MPa. . After being treated by the acetaldehyde rectification column, high-purity acetaldehyde is collected at the top of the column, and the bottom wastewater is directly passed through another separate line to enter the ethylene glycol separation tower of the esterification unit, and the line enters the separation tower body at a position The 12th tray; the ratio of the amount of waste water in the bottom of the acetaldehyde rectification tower to the original reflux flow rate of the separation tower is 0.6; the separation of ethylene glycol and water and other organic substances is completed in the separation tower, and the recovered ethylene glycol directly enters the esterification. The reaction kettle continues the esterification reaction; (3) The esterified wastewater or steam from which the organic matter is collected from the top of the esterification separation column, and again enters the stripping column for treatment.

經本發明提供的技術流程裝置進行處理得到各產物組分及其含量,如表3所示。 The product components and their contents were obtained by the technical flow device provided by the present invention, as shown in Table 3.

實施例4 Example 4

(1)從酯化單元乙二醇分離塔出來的酯化廢水(COD為28000mg/L)和蒸汽進入氣提塔處理,氣提塔的熱傳質為水蒸氣,壓力為0.6MPa,塔頂壓力為0.5MPa,塔頂溫度為100℃;塔底溫度為120℃,在塔頂收集到的有機物氣體與水蒸氣進入乙醛精餾塔,在氣提塔塔底收集的廢水COD值為2455mg/L; (2)乙醛精餾塔的熱源為水蒸氣,壓力為0.6MPa,塔頂壓力為0.6MPa,塔頂溫度為100℃,塔底溫度為120℃,回流比為6,操作壓力為0.5MPa。經乙醛精餾塔處理後,在塔頂收集到高純度乙醛,塔底廢水則直接通過另外單獨走線進入酯化單元的乙二醇分離塔,該線路進入分離塔塔體的位置位於第6塊塔板;乙醛精餾塔塔底廢水量與分離塔原回流量之比為0.6;在分離塔內完成乙二醇和水及其他有機物的分離,回收得到的乙二醇直接進入酯化反應釜,繼續進行酯化反應; (3)從酯化分離塔頂出來的收集了有機物的酯化廢水或蒸汽,再次進入氣提塔迴圈處理。 (1) The esterification wastewater (COD is 28000 mg/L) from the esterification unit ethylene glycol separation tower and steam are sent to the stripping tower for treatment. The heat transfer mass of the stripping tower is water vapor, and the pressure is 0.6 MPa. The pressure is 0.5MPa, the temperature at the top of the tower is 100°C, the temperature at the bottom of the column is 120°C, the organic gas and water vapor collected at the top of the tower enter the acetaldehyde rectification tower, and the COD value of the wastewater collected at the bottom of the stripping tower is 2455mg. /L; (2) The heat source of the acetaldehyde rectification column is water vapor, the pressure is 0.6 MPa, the top pressure is 0.6 MPa, the top temperature is 100 ° C, the bottom temperature is 120 ° C, the reflux ratio is 6, and the operating pressure is 0.5 MPa. . After being treated by the acetaldehyde rectification column, high-purity acetaldehyde is collected at the top of the column, and the bottom wastewater is directly passed through another separate line to enter the ethylene glycol separation tower of the esterification unit, and the line enters the separation tower body at a position The sixth tray; the ratio of the amount of waste water in the bottom of the acetaldehyde distillation tower to the original reflux flow of the separation tower is 0.6; the separation of ethylene glycol and water and other organic substances is completed in the separation tower, and the recovered ethylene glycol directly enters the esterification. The reaction kettle continues the esterification reaction; (3) The esterified wastewater or steam from which the organic matter is collected from the top of the esterification separation column, and again enters the stripping column for treatment.

經本發明提供的技術流程裝置進行處理得到各產物組分及其含量,如表4所示。 The product components and their contents were obtained by the technical flow device provided by the present invention, as shown in Table 4.

實施例5 Example 5

改進前的處理技術流程實施效果。 The effect of the implementation of the processing technology flow before the improvement.

改進前的技術及裝置(採用附圖1流程)已經在聚酯行業的知名企業得到了實際應用。以年產15萬噸聚酯產生的酯化廢水為例,改進前具體技術結果如表5所述:表5 酯化廢水及產物各組分含量 The technology and equipment before the improvement (using the process of Figure 1) have been put into practical use in well-known enterprises in the polyester industry. Taking the esterification wastewater produced by an annual output of 150,000 tons of polyester as an example, the specific technical results before the improvement are as shown in Table 5: Table 5 Esterification wastewater and the content of each component of the product

實施例6 Example 6

本發明(改進後)處理技術流程實施效果。 The present invention (improved) processes the technical process implementation effects.

本發明技術及裝置(採用附圖2流程)已經在聚酯行業的知名企業得到了實際應用,操作條件同實施例4所描述。以年產15萬噸聚酯產生的酯化廢水為例,改進後具體技術結果如下所述: 根據實際生產情況,將所得的酯化廢水,經本發明提供的技術流程裝置進行處理得到各產物組分及其含量,如表6所示。 The technology and device of the present invention (using the flow of FIG. 2) have been put into practical use in well-known enterprises in the polyester industry, and the operating conditions are as described in Embodiment 4. Taking the esterification wastewater produced by an annual output of 150,000 tons of polyester as an example, the specific technical results after improvement are as follows: According to the actual production conditions, the obtained esterified wastewater was treated by the technical flow device provided by the present invention to obtain the product components and their contents, as shown in Table 6.

由處理後的結果可以看出:在經過本技術流程的廢水處理系統處理後,不論從乙醛和乙二醇的產量,還是排放廢水指標來看,絲毫沒有影響產品的各項指標,回收得到的乙二醇純度反而更高,這充分說明改進後的發明技術流程是成功的、可行的。 It can be seen from the processed results that after treatment with the wastewater treatment system of the technical process, regardless of the output of acetaldehyde and ethylene glycol or the discharge wastewater index, the products have no influence on the various indexes, and the recovery is obtained. The purity of the ethylene glycol is rather higher, which fully demonstrates that the improved inventive process is successful and feasible.

表7改進前後蒸汽消耗對比表(折合成蒸汽消耗) Table 7 Comparison of steam consumption before and after improvement (converted to steam consumption)

表7列出了改進前後蒸汽消耗情況,通過兩次對比資料,不難看出,改進後,蒸汽消耗顯著降低26%,達到了節能降耗的目的。因此,本發明的技術流程及裝置能夠使得本技術的推廣邁向一個嶄新的臺階,從而為企業、為社會創造更大的效益。 Table 7 lists the steam consumption before and after the improvement. It is easy to see through two comparisons. After the improvement, the steam consumption is significantly reduced by 26%, achieving the goal of energy saving. Therefore, the technical process and device of the present invention can make the promotion of the technology to a new stage, thereby creating greater benefits for enterprises and society.

應該理解以上的敍述對於如申請專利範圍所闡述的本發明僅僅是示例和說明性的,並非對其加以限制。根據本文所披露的本發明的內容,本發明的其他實施方案對於本領域的技術人員來說是顯而易見的。應該指出的是本說明書和實施例僅應被看做為示例,本發明的實際範圍由申請專利範圍確定。 The above description is to be construed as illustrative and not restrictive Other embodiments of the invention will be apparent to those skilled in the art from this disclosure. It should be noted that the present specification and examples are to be considered as illustrative only, and the actual scope of the invention is determined by the scope of the claims.

1‧‧‧氣提塔 1‧‧‧Flat Tower

101‧‧‧蒸汽 101‧‧‧Steam

2‧‧‧乙醛精餾塔 2‧‧‧acetaldehyde distillation tower

201‧‧‧蒸汽 201‧‧‧Steam

202‧‧‧廢水收集裝置 202‧‧‧Waste collection device

203‧‧‧蒸汽回收裝置 203‧‧‧Steam recovery unit

Claims (10)

一種聚酯廢水中回收乙二醇和乙醛的方法,是一個連續收集的過程,其特徵在於是通過以下的步驟實現的:(1)酯化廢水進入氣提塔處理,在塔底得到氣提廢水進行污水處理,在塔頂收集到的有機物氣體進入乙醛精餾塔;(2)經乙醛精餾塔處理後,在塔頂收集到高純度乙醛,塔底收集到的廢水進入原有酯化單元的乙二醇分離塔,在分離塔內完成乙二醇和水及其他有機物的分離,回收得到的乙二醇直接進入酯化反應釜,繼續進行酯化反應;以及(3)從酯化單元的乙二醇分離塔頂出來的收集了有機物的酯化廢水或蒸汽,再次進入氣提塔迴圈處理。 A method for recovering ethylene glycol and acetaldehyde in polyester wastewater is a continuous collection process, which is characterized by the following steps: (1) the esterification wastewater is treated in a stripping tower, and stripping is obtained at the bottom of the column. The wastewater is treated by sewage, and the organic gas collected at the top of the tower enters the acetaldehyde rectification column; (2) after being treated by the acetaldehyde rectification column, high-purity acetaldehyde is collected at the top of the tower, and the wastewater collected at the bottom of the tower enters the original a glycol separation column having an esterification unit, which separates ethylene glycol from water and other organic substances in the separation column, and the recovered ethylene glycol directly enters the esterification reactor to continue the esterification reaction; and (3) The esterification wastewater or steam collected from the ethylene glycol separation tower of the esterification unit is collected and returned to the stripping column for treatment. 如申請專利範圍第1項所述之聚酯廢水中回收乙二醇和乙醛的方法,其中該步驟(1)中所述的酯化廢水包含了原有酯化廢水和步驟(3)中得到的廢水或蒸汽,其COD值不小於20000mg/L。 The method for recovering ethylene glycol and acetaldehyde in the polyester wastewater according to claim 1, wherein the esterification wastewater described in the step (1) comprises the original esterification wastewater and is obtained in the step (3). The wastewater or steam has a COD value of not less than 20,000 mg/L. 如申請專利範圍第1項所述之聚酯廢水中回收乙二醇和乙醛的方法,其中該步驟(1)中所述的氣提塔的熱源為水蒸氣,壓力為0.1-1.0MPa,塔頂壓力為0.1-1.0MPa,塔頂溫度為60-140℃;塔底溫度為80-160℃。 The method for recovering ethylene glycol and acetaldehyde in the polyester wastewater according to claim 1, wherein the heat source of the stripping tower described in the step (1) is water vapor, and the pressure is 0.1-1.0 MPa. The top pressure is 0.1-1.0 MPa, the top temperature is 60-140 ° C, and the bottom temperature is 80-160 ° C. 如申請專利範圍第1項所述之聚酯廢水中回收乙二醇和乙醛的方法,其中該步驟(1)中所述的在塔頂收集到的有機物氣體經冷凝後以液體方式用泵打進乙醛精餾塔,或者不經冷凝直接進入乙醛精餾塔。 The method for recovering ethylene glycol and acetaldehyde in the polyester wastewater according to claim 1, wherein the organic gas collected at the top of the step described in the step (1) is condensed and pumped in a liquid manner. Into the acetaldehyde rectification column, or directly into the acetaldehyde rectification column without condensation. 如申請專利範圍第1項所述之聚酯廢水中回收乙二醇和乙醛的方法,其中該氣提塔在塔底收集的廢水COD小於3000mg/L。 The method for recovering ethylene glycol and acetaldehyde in the polyester wastewater according to claim 1, wherein the waste water collected by the stripping tower at the bottom of the tower has a COD of less than 3000 mg/L. 如申請專利範圍第1項所述之聚酯廢水中回收乙二醇和乙醛的方法,其中該步驟(2)中所述的乙醛精餾塔的熱源為水蒸氣,壓力為0.1-1.0MPa,塔頂壓力為0.1-1.0MPa,塔頂溫度為20-80℃,塔底溫度為80-160℃,回流比為0.1-50,操作壓力為0.1-1.0MPa。 The method for recovering ethylene glycol and acetaldehyde in the polyester wastewater according to claim 1, wherein the heat source of the acetaldehyde rectification column described in the step (2) is water vapor, and the pressure is 0.1-1.0 MPa. The pressure at the top of the column is 0.1-1.0 MPa, the temperature at the top of the column is 20-80 ° C, the temperature at the bottom of the column is 80-160 ° C, the reflux ratio is 0.1-50, and the operating pressure is 0.1-1.0 MPa. 如申請專利範圍第1項所述之聚酯廢水中回收乙二醇和乙醛的方法,其中該乙醛精餾塔塔底廢水通過乙二醇分離塔的回流或 另外通過管道進入乙二醇分離塔。 The method for recovering ethylene glycol and acetaldehyde in the polyester wastewater according to claim 1, wherein the acetaldehyde distillation tower bottom wastewater is refluxed by the ethylene glycol separation column or In addition, it enters the glycol separation column through a pipe. 如申請專利範圍第7項所述之聚酯廢水中回收乙二醇和乙醛的方法,其中該乙醛精餾塔塔底廢水量與乙二醇分離塔原回流量之比不超過1。 The method for recovering ethylene glycol and acetaldehyde in the polyester wastewater according to claim 7, wherein the ratio of the bottom amount of the acetaldehyde distillation column to the original reflux flow rate of the ethylene glycol separation column is not more than 1. 如申請專利範圍第7項所述之聚酯廢水中回收乙二醇和乙醛的方法,其中該乙醛精餾塔塔底廢水另外通過管道進入乙二醇分離塔塔體的位置位於第1-12塊塔板之間。 The method for recovering ethylene glycol and acetaldehyde in the polyester wastewater according to claim 7 of the patent application, wherein the bottom of the acetaldehyde distillation tower bottom water is additionally connected to the ethylene glycol separation tower by a pipeline. Between 12 trays. 如申請專利範圍第1至9項任一項所述的一種聚酯廢水中回收乙二醇和乙醛的方法,其特徵在於步驟(2)中所述的乙醛精餾塔塔底廢水中含有少量未分解的2-甲基-1,3-二氧戊環和乙醛蒸汽重新進入酯化單元乙二醇分離塔、氣提塔、乙醛精餾塔進行迴圈分解並進一步處理。 A method for recovering ethylene glycol and acetaldehyde in a polyester wastewater according to any one of claims 1 to 9, characterized in that the acetaldehyde distillation column bottom wastewater described in the step (2) contains A small amount of undecomposed 2-methyl-1,3-dioxolane and acetaldehyde vapors are re-entered into the esterification unit ethylene glycol separation column, stripping column, and acetaldehyde rectification column for loop decomposition and further processing.
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