CN100415654C - Process for purifying and resource recovery using from waste water of producing H cide - Google Patents

Process for purifying and resource recovery using from waste water of producing H cide Download PDF

Info

Publication number
CN100415654C
CN100415654C CNB2005100376970A CN200510037697A CN100415654C CN 100415654 C CN100415654 C CN 100415654C CN B2005100376970 A CNB2005100376970 A CN B2005100376970A CN 200510037697 A CN200510037697 A CN 200510037697A CN 100415654 C CN100415654 C CN 100415654C
Authority
CN
China
Prior art keywords
acid
waste water
resin
tower
desorption
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Expired - Fee Related
Application number
CNB2005100376970A
Other languages
Chinese (zh)
Other versions
CN1693219A (en
Inventor
陈金龙
张炜铭
张波
张全兴
鲁俊东
潘丙才
李爱民
费正皓
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Jiangsu N&J Environmental Technology Co., Ltd.
Nanjing University
Original Assignee
Jiangsu Nju Gede Environmental Protection Technology Co Ltd
Nanjing University
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Jiangsu Nju Gede Environmental Protection Technology Co Ltd, Nanjing University filed Critical Jiangsu Nju Gede Environmental Protection Technology Co Ltd
Priority to CNB2005100376970A priority Critical patent/CN100415654C/en
Publication of CN1693219A publication Critical patent/CN1693219A/en
Application granted granted Critical
Publication of CN100415654C publication Critical patent/CN100415654C/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Abstract

The present invention discloses a method for recovering sources and purifying waste water of H acid production. Filtrated waste water of H acid production passes through an absorbing column containing resin. Thus, the H acid and the T acid in the waste water of H acid production are absorbed on the resin. Thus, the effective separation of organic substances and a sodium sulfate saturated solution is realized. The yielding water after adsorptive separation is a transparent saturated sodium sulfate solution without color. The solution can be recovered for the flushing work procedures of T acid and H acid filtering cakes of the original producing technology. The resin after the absorbing operation is eluted and regenerated by an aqueous sodium hydroxide solution. The high-concentration sodium solution of the H acid and the T acid after desorption returns to the alkali fusion work procedure of the original producing technology. Desorption liquid of low concentration can be used for preparing the aqueous sodium hydroxide solution to be used for the desorption operation of the next batch. The present invention separates and reuses the saturated sodium sulfate solution from the waste water of H acid production. Meanwhile, the H acid and the T acid are recovered. Thus, the unification of the treatment and the reuse of the waste water and the purpose of changing waste into resources are realized. The present invention has great practical value and economic value in the producing process of the H acid.

Description

The purification of H acid producing waste water and the method for resource recycling
One, technical field
The present invention relates to the recoverying and utilizing method of useful resources in the purification of waste water of being discharged in a kind of H acid production process and the waste water.Specifically, be exactly a kind of from the H acid producing waste water separating and recovering sodium sulfate saturated solution, from waste water, reclaim the method for useful resources H acid and T acid simultaneously.
Two, background technology
H acid is 1-amino-8-naphthol-3, the 6-disulfonic acid (chemical structural formula is:
Figure C20051003769700031
), be important naphthalene series dye intermediate, it is mainly used in and produces directly, acid, reactive dyestuffs and azoic dyestuff intermediate, as acid day blue, direct kind surplus the black Reactive Brilliant Red K-2BP etc. 90, also can be used for pharmaceutical industry.At present, the production technique of domestic H acid generally is to be raw material with the refined naphthalene, makes through operations such as sulfonation, nitrated, neutralization, reduction, alkali fusion and acid outs.Produced COD in the production process CrUp to the waste water of 20000~30000mg/L, contain the sodium sulfate of saturation concentration in the waste water, wherein organic composition is mainly product H acid and intermediate T acid.Because it is very high that H acid and T acid are difficult in biological degradation, the water-soluble very big again and waste water sodium sulphate content, thereby the cost-effective improvement of H acid producing waste water is the generally acknowledged difficult problem of domestic and international environmental protection circle always.The manufacturing enterprise of H acid both at home and abroad at present mainly adopts this waste water of dilution-biochemical treatment, and H acid and the T acid in the water body at this moment is broken to small-molecule substance and causes the wasting of resources in treating processes.
Three, summary of the invention
The purpose of this invention is to provide a kind of purification of H acid producing waste water and the method for resource recycling, this method can make waste water after resin absorption is separated, in reuse sodium sulfate saturated solution, reclaim wherein T acid, H acid, realize the combination of waste water treatment and resource recycling.
The objective of the invention is to be achieved through the following technical solutions:
A kind of purification of H acid producing waste water and the method for resource recycling is characterized in that it may further comprise the steps:
A) the H acid producing waste water is filtered, remove suspended substance wherein; Raw wastewater among the present invention is the sodium sulfate saturated solution that slightly is muddy shape, and wherein, the H acid concentration is 2000~4000mg/L, and the T acid concentration is 14000~17000mg/L, COD CrBe 20000~30000mg/L.
B) with steps A) filtrate that obtains is by being filled with the macroporous resin absorption tower, and H acid and T acid in the waste water optionally are adsorbed on the resin, and absorption effluent is water white sodium sulfate saturated solution; The present invention can be at 5~45 ℃ with steps A) filtrate that obtains with the flow of 0.5~3BV/h (BV is the resin bed volume) by being filled with the macroporous resin absorption tower.Described resin is to be the macroporous resin of basic framework with the polystyrene, it can be ND-910 complexing polymeric adsorbent, NDA-99 and NDA-88 composite function resin (Jiangsu Nanda Gede Environmental Protection Technology Co., Ltd's production) and D301 resin (production such as Langfang, Hebei electric power resin processing plant), also can be the macroporous resins such as Amberlite IRA96, IRA93 that U.S. RohmHaas company produces, ND-910 complexing polymeric adsorbent preferably wherein.Water white sodium sulfate saturated solution can be back to T acid, the H acidleach of original production process among the present invention
Cake flushing operation.
C) when absorption reaches leakage point, stop absorption, as desorbing agent, carry out desorption and regeneration, obtain the sodium salt solution of high density H acid, T acid with aqueous sodium hydroxide solution; Naoh concentration of the present invention can be 2%~10%, carries out desorption and regeneration at 30~55 ℃ of flows with 0.5~2BV/h.For guaranteeing the quality of desorption and regeneration, for saving cost, the present invention carries out the resin desorption and regeneration after polymeric adsorbent has been handled 5~10BV/ batch waste water on the other hand on the one hand.
D) will be by step C) the desorption high density H acid of getting off, the sodium salt solution of T acid returns the alkali fusion procedure of original production process, and light concentration desorption liquid is used to prepare the aqueous sodium hydroxide solution cover and is used for the next batch desorption manipulation.
The present invention is at step B) described in adsorption tower can adopt the operation scheme of double-column in series absorption, single tower desorption; I, II, three adsorption towers of III are set, and with I, II tower series connection following current absorption, the I tower is as first post earlier, the II tower after the absorption of I tower is saturated, switches to II, III tower series connection following current absorption as stern post, the II tower is as first post, and the III tower is as stern post, and the I tower carries out desorption and regeneration with desorbing agent simultaneously.
According to method provided by the invention, (slightly muddy, the H acid concentration is 2000~4000mg/L to raw wastewater, and the T acid concentration is 14000~17000mg/L, COD CrBe the sodium sulfate saturated solution of 20000~30000mg/L) after resin absorption was separated, water outlet was water white sodium sulfate saturated solution, H acid concentration<20mg/L, T acid concentration<30mg/L, COD Cr<650mg/L, T acid, the H acidleach cake that can be back to original production process wash operation; Can from every cubic metre of waste water, reclaim simultaneously about 2 kilograms of H acid, about 10 kilograms of T acid.The present invention has realized the separation and the recycling of pollutent when administering waste water.
Resin absorption operation among the present invention can be adopted the operation scheme of double-column in series absorption, single tower desorption, moves continuously to guarantee whole waste water treatment device.Compared with prior art, beneficial effect of the present invention is: 1, the water outlet after fractionation by adsorption of H acid producing waste water is water white sodium sulfate saturated solution, H acid concentration<20mg/L, T acid concentration<30mg/L, COD Cr<650mg/L, T acid, the H acidleach cake that can be back to original production process wash operation; 2, most H acid and T acid in the separable recovery raw wastewater realizes the resource recycling; 3, the polymeric adsorbent regenerability is good, and is reusable.
Four, embodiment
By the following examples the present invention is further described:
Embodiment 1
10mL (about 6.8 gram) macropore complexing polymeric adsorbent NDA-910 packed in the glass adsorption column of strap clamp cover, and (Φ 12 * 160mm).Waste water COD CrBe 23000mg/L, after the filtration, in 15 ± 5 ℃, by resin bed, treatment capacity is that 70mL/ criticizes with the flow of 10mL/h with it.After resin absorption, the water outlet water white transparency, the H acid concentration is 14mg/L, the T acid concentration is 25mg/L, COD CrBe 550mg/L.
The 20mL4% aqueous sodium hydroxide solution under 45 ± 5 ℃ temperature, is carried out desorption with the flow following current of 5mL/h by resin bed.The high density H acid that desorption gets off, the sodium salt solution of T acid can return the alkali fusion procedure of original production process.Light concentration desorption liquid is used to prepare the used aqueous sodium hydroxide solution of next batch desorption.
Embodiment 2
100mL (about 68 gram) NDA-910 resin packed in the glass adsorption column of strap clamp cover, and (Φ 32 * 260mm).Waste water COD CrBe 22000mg/L, after the filtration, in 40 ± 5 ℃, by resin bed, treatment capacity is that 700mL/ criticizes with the flow of 150mL/h with it.After resin absorption, the water outlet water white transparency, the H acid concentration is 15mg/L, the T acid concentration is 23mg/L, COD CrBe 500mg/L.
The 100mL10% aqueous sodium hydroxide solution under 35 ± 5 ℃ temperature, is carried out desorption with the flow following current of 50mL/h by resin bed.The high density H acid that desorption gets off, the sodium salt solution of T acid can return the alkali fusion procedure of original production process.Light concentration desorption liquid is used to prepare the used aqueous sodium hydroxide solution of next batch desorption.
Embodiment 3
1000mL (about 680 gram) ND-910 resin packed in the glass adsorption column of strap clamp cover, and (Φ 70 * 500mm).Waste water COD CrBe 24000mg/L, after the filtration, in 15 ± 5 ℃, by resin bed, treatment capacity is that 6000mL/ criticizes with the flow of 2500mL/h with it.After resin absorption, the water outlet water white transparency, the H acid concentration is 18mg/L, the T acid concentration is 27mg/L, COD CrBe 620mg/L.
The 1500mL6% aqueous sodium hydroxide solution under 40 ± 5 ℃ temperature, is carried out desorption with the flow following current of 1000mL/h by resin bed.The high density H acid that desorption gets off, the sodium salt solution of T acid can return the alkali fusion procedure of original production process.Light concentration desorption liquid is used to prepare the used aqueous sodium hydroxide solution of next batch desorption.
Embodiment 4
Select that three specifications are identical, material is 316L stainless steel adsorption tower for use (Φ 550 * 3500mm), compile Shang number be respectively I, II and III, every tower loads 340 kilograms of (about 0.5m of NDA-910 polymeric adsorbent 3).Waste water COD CrBe 24000mg/L, after the filtration, with it in 20 ± 5 ℃, with 0.5m 3The flow of/h is squeezed into adsorption tower with pump, and the mode of I, II tower double-column in series following current absorption is adopted in absorption, and treatment capacity is 3.5m 3/ batch.After resin absorption, the water outlet water white transparency, the H acid concentration is 15mg/L, the T acid concentration is 25mg/L, COD CrBe 550mg/L.
To adsorb 3.5m 3The first post I adsorption tower of waste water breaks away from absorption system and carries out desorption manipulation; And the next batch adsorption operations changes II, the series operation of III tower into, post headed by the II tower becomes.
Earlier raffinate in the I adsorption tower is drained, again with 0.75m 38% aqueous sodium hydroxide solution is under 35 ± 5 ℃ temperature, with 0.25m 3The flow following current of/h is carried out desorption by resin bed.The high concentration desorption liquid that desorption gets off is back to the alkali fusion procedure of original production process.Light concentration desorption liquid is used to prepare the aqueous sodium hydroxide solution cover and is used for the next batch desorption manipulation.
I adsorption tower after desorption finishes will be as the stern post of the 3rd batch of adsorption operations.Can guarantee that by the present invention whole waste water treatment device moves continuously.
Embodiment 5
Change the NDA-910 resin among the embodiment 1 domestic resins such as into NDA-99, NDA-88, NDA-100 and D301, or resin and macroporous weak such as U.S. AmberliteIRA93, IRA96, other operational conditions remain unchanged, except that every batch processing volume and absorption effluent water quality decreased, other effects substantially roughly the same.

Claims (8)

1. the method for the purification of a H acid producing waste water and resource recycling is characterized in that said method comprising the steps of:
A) the H acid producing waste water is filtered, remove suspended substance wherein;
B) with steps A) filtrate that obtains is by being filled with the macroporous resin absorption tower, and H acid and T acid in the waste water optionally are adsorbed on the resin, and absorption effluent is water white sodium sulfate saturated solution;
C) when absorption reaches leakage point, stop absorption, as desorbing agent, carry out desorption and regeneration, obtain the sodium salt solution of high density H acid and T acid with aqueous sodium hydroxide solution;
D) will be by step C) the high density H acid that desorption gets off and the sodium salt solution of T acid return the alkali fusion procedure of original production process, and the desorption liquid of remainder is used to prepare the aqueous sodium hydroxide solution cover and is used for the next batch desorption manipulation.
2. the purification of H acid producing waste water according to claim 1 and the method for resource recycling, it is characterized in that: step B), at 5~45 ℃ with steps A) filtrate that obtains with the flow of 0.5~3 resin bed volume per hour by being filled with the macroporous resin absorption tower.
3. the purification of H acid producing waste water according to claim 1 and the method for resource recycling, it is characterized in that: resin step B) is to be the macroporous resin of basic framework with the polystyrene, and described macroporous resin is Amberlite IRA96, the IRA93 macroporous resin that ND-910 complexing polymeric adsorbent, NDA-99 and NDA-88 composite function resin, D301 resin or U.S. Rohm Haas company produce.
4. the purification of H acid producing waste water according to claim 3 and the method for resource recycling is characterized in that: described resin is a ND-910 complexing polymeric adsorbent.
5. the purification of H acid producing waste water according to claim 1 and the method for resource recycling is characterized in that: step B), described sodium sulfate saturated solution is back to the T acid and the H acidleach cake flushing operation of original production process.
6. the purification of H acid producing waste water according to claim 1 and the method for resource recycling, it is characterized in that: step C), sodium hydroxide concentration is 2%~10%, carries out desorption and regeneration at 30~55 ℃ with the flow of 0.5~2 resin bed volume per hour.
7. the purification of H acid producing waste water according to claim 1 and the method for resource recycling is characterized in that: step C), polymeric adsorbent be in every batch processed carry out the resin desorption and regeneration behind the waste water of 5~10 resin bed volumes.
8. the purification of H acid producing waste water according to claim 1 and the method for resource recycling is characterized in that: adsorption tower step B) adopts the operation scheme of double-column in series absorption, single tower desorption; Three adsorption towers of I and II and III are set, and with I and II tower series connection following current absorption, the I tower is as first post earlier, the II tower after the absorption of I tower is saturated, switches to II and III tower series connection following current absorption as stern post, the II tower is as first post, and the III tower is as stern post, and the I tower carries out desorption and regeneration with desorbing agent simultaneously.
CNB2005100376970A 2005-01-13 2005-01-13 Process for purifying and resource recovery using from waste water of producing H cide Expired - Fee Related CN100415654C (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CNB2005100376970A CN100415654C (en) 2005-01-13 2005-01-13 Process for purifying and resource recovery using from waste water of producing H cide

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CNB2005100376970A CN100415654C (en) 2005-01-13 2005-01-13 Process for purifying and resource recovery using from waste water of producing H cide

Publications (2)

Publication Number Publication Date
CN1693219A CN1693219A (en) 2005-11-09
CN100415654C true CN100415654C (en) 2008-09-03

Family

ID=35352366

Family Applications (1)

Application Number Title Priority Date Filing Date
CNB2005100376970A Expired - Fee Related CN100415654C (en) 2005-01-13 2005-01-13 Process for purifying and resource recovery using from waste water of producing H cide

Country Status (1)

Country Link
CN (1) CN100415654C (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108128950A (en) * 2017-10-11 2018-06-08 盐城市凌意环保科技有限公司 A kind of processing unit and its processing method of H acid waste water

Families Citing this family (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101104533B (en) * 2007-06-05 2011-07-27 南开大学 Method for treating waste water of H-acid production
CN101066824B (en) * 2007-06-14 2010-10-27 南开大学 Process of treating and reusing effluent from 1-amino-8-naphthol-3, 6-disulfonic acid production
CN102910853B (en) * 2011-08-03 2018-06-19 浙江龙盛化工研究有限公司 A kind of method using H acid Sewage treatments liquid production naphthalene series high-efficiency water-reducing agent
CN102775808B (en) * 2012-08-23 2013-08-21 楚源高新科技集团股份有限公司 Process for recycling ammonium sulfate and synthesizing acidic dye by T-acid mother liquor wastewater
CN106380022B (en) * 2016-11-27 2019-04-05 南京悠谷知识产权服务有限公司 A kind for the treatment of process of H acid producing waste water, device and dedicated absorption resin material

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH06304403A (en) * 1993-04-27 1994-11-01 Mitsubishi Kasei Corp Decoloration
JPH08150400A (en) * 1994-11-29 1996-06-11 Japan Organo Co Ltd Device for treating waste water containing organic matter
CN1265376A (en) * 2000-03-13 2000-09-06 南京大学 Treatment of 2,3-acid producing waste water and resource recovering and utilizing method
CN1384069A (en) * 2001-07-18 2002-12-11 南京大学 Method of treating naphthalene-blowing effluence and recovering resource in 2-naphthol producing process
CN1537816A (en) * 2003-10-24 2004-10-20 南京大学 Treatment of waste water in producing isophthalic acid dicarbomethoxy-5-sodium sulphonate and its resource utilization method

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH06304403A (en) * 1993-04-27 1994-11-01 Mitsubishi Kasei Corp Decoloration
JPH08150400A (en) * 1994-11-29 1996-06-11 Japan Organo Co Ltd Device for treating waste water containing organic matter
CN1265376A (en) * 2000-03-13 2000-09-06 南京大学 Treatment of 2,3-acid producing waste water and resource recovering and utilizing method
CN1384069A (en) * 2001-07-18 2002-12-11 南京大学 Method of treating naphthalene-blowing effluence and recovering resource in 2-naphthol producing process
CN1537816A (en) * 2003-10-24 2004-10-20 南京大学 Treatment of waste water in producing isophthalic acid dicarbomethoxy-5-sodium sulphonate and its resource utilization method

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
大孔弱碱性树脂对高水溶性磺酚类染料中间体的吸附. 龙超,张全兴,陈金龙.应用化学,第21卷第10期. 2004 *
氨基萘本分磺酸在改性超高交联吸附树脂和弱碱树脂上的静态吸附行为比较. 刘福强,陈金龙,李爱民,张全兴.高分子学报,第5期. 2004 *

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108128950A (en) * 2017-10-11 2018-06-08 盐城市凌意环保科技有限公司 A kind of processing unit and its processing method of H acid waste water

Also Published As

Publication number Publication date
CN1693219A (en) 2005-11-09

Similar Documents

Publication Publication Date Title
CN101104533B (en) Method for treating waste water of H-acid production
CN104876380B (en) A kind of processing of organic copper-containing wastewater of high concentration and the recovery method of copper
CN1295155C (en) Treatment of wastewater from production of p-phthalic acid and recoval of resources therewith
CN102992433B (en) Extraction recovery method of waste water produced by naphthalene-series dye intermediate
CN100415654C (en) Process for purifying and resource recovery using from waste water of producing H cide
CN101774730B (en) Intermediate waste water treatment method of quinacridone pigment and modified macroporous absorbent resin used by method
CN1712365A (en) Treatment of wastewater from production of para-aminophenol and making it be resource
CN101519249B (en) Method for treating hydrolyzed waste water and recovering resource in disperse blue production process
CN104671537A (en) Method for treating mother liquor wastewater generated in one-time nitrifying and refining of disperse blue 56
CN101269798A (en) Method for recycling organic resource in waste sulphuric acid and refining waste sulfuric acid
CN105110544A (en) Method for treating wastewater with dilute alkali by aid of macroporous resin
CN105084600A (en) Method for efficiently treating salt-containing organic wastewater and application of method
CN100453523C (en) Method for treating diethyl (o-) phthalate waste water and recovering diethyl (o-) phthalate from it
CN100334016C (en) Method for treating waste water from meta dinitro benzene production
CN101665298B (en) Method for removing phthalate ester in water body by utilizing solid base catalyst
CN104445781B (en) A kind of administering method of fused ring compound waste water
CN100352770C (en) Integrated process for treating waste water of p-aminophenol production and resource recovery method
CN1762991A (en) Adsorption treating method for resinifying sulfonated waste acid in DSD acid production
CN100560512C (en) A kind of 4,4-diaminobenzil-2, the 2-disulfonic acid is produced the improvement and the method for resource of oxidized waste water
CN1156407C (en) Treatment and rediaimation of waste water in production of 4,4'-dinitrobistyrene-2,2'-bisulfonic acid
CN1147437C (en) Method for treating waste water in dinaphthyl phenol production
CN102874944B (en) Method for treating dye wastewater
CN102923821B (en) Treatment method of wastewater of oxalic acid production
CN103539285A (en) Treating method for recycling wastewater of N-methylaniline production
CN1323041C (en) Waste water treating and resourcelization method for tobias acid production

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
C56 Change in the name or address of the patentee
CP01 Change in the name or title of a patent holder

Address after: 210093 Department of environmental science, Nanjing University, 22 Hankou Road, Jiangsu, Nanjing

Co-patentee after: Jiangsu N&J Environmental Technology Co., Ltd.

Patentee after: Nanjing University

Address before: 210093 Department of environmental science, Nanjing University, 22 Hankou Road, Jiangsu, Nanjing

Co-patentee before: Jiangsu NJU Gede Environmental Protection Technology Co., Ltd.

Patentee before: Nanjing University

C17 Cessation of patent right
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20080903

Termination date: 20140113