CN1911906A - Method of separating and recovering 2-naphthalenesulfonic acid from waste water of 2-naphthol production - Google Patents
Method of separating and recovering 2-naphthalenesulfonic acid from waste water of 2-naphthol production Download PDFInfo
- Publication number
- CN1911906A CN1911906A CN200610088490.0A CN200610088490A CN1911906A CN 1911906 A CN1911906 A CN 1911906A CN 200610088490 A CN200610088490 A CN 200610088490A CN 1911906 A CN1911906 A CN 1911906A
- Authority
- CN
- China
- Prior art keywords
- resin
- sulfonic acid
- effluent
- waste water
- naphthene sulfonic
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
- 238000000034 method Methods 0.000 title claims abstract description 14
- 239000002351 wastewater Substances 0.000 title claims description 21
- 238000004519 manufacturing process Methods 0.000 title abstract description 5
- JWAZRIHNYRIHIV-UHFFFAOYSA-N 2-naphthol Chemical compound C1=CC=CC2=CC(O)=CC=C21 JWAZRIHNYRIHIV-UHFFFAOYSA-N 0.000 title abstract 8
- KVBGVZZKJNLNJU-UHFFFAOYSA-N naphthalene-2-sulfonic acid Chemical compound C1=CC=CC2=CC(S(=O)(=O)O)=CC=C21 KVBGVZZKJNLNJU-UHFFFAOYSA-N 0.000 title abstract 6
- 229950011260 betanaphthol Drugs 0.000 title abstract 4
- 229920005989 resin Polymers 0.000 claims abstract description 34
- 239000011347 resin Substances 0.000 claims abstract description 34
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims abstract description 24
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 15
- 238000001179 sorption measurement Methods 0.000 claims abstract description 9
- 238000001914 filtration Methods 0.000 claims abstract description 4
- LSNNMFCWUKXFEE-UHFFFAOYSA-M Bisulfite Chemical compound OS([O-])=O LSNNMFCWUKXFEE-UHFFFAOYSA-M 0.000 claims description 18
- PJKVFARRVXDXAD-UHFFFAOYSA-N 2-naphthaldehyde Chemical compound C1=CC=CC2=CC(C=O)=CC=C21 PJKVFARRVXDXAD-UHFFFAOYSA-N 0.000 claims description 13
- 239000003795 chemical substances by application Substances 0.000 claims description 9
- 238000003795 desorption Methods 0.000 claims description 8
- 238000011084 recovery Methods 0.000 claims description 7
- 238000000926 separation method Methods 0.000 claims description 6
- 238000010521 absorption reaction Methods 0.000 claims description 5
- -1 acrylic ester Chemical class 0.000 claims description 5
- 239000003463 adsorbent Substances 0.000 claims description 5
- 238000011010 flushing procedure Methods 0.000 claims description 5
- 229920001429 chelating resin Polymers 0.000 claims description 3
- 239000007788 liquid Substances 0.000 claims description 3
- 238000002203 pretreatment Methods 0.000 claims description 3
- 230000008929 regeneration Effects 0.000 claims description 3
- 238000011069 regeneration method Methods 0.000 claims description 3
- 238000001816 cooling Methods 0.000 claims description 2
- 239000013078 crystal Substances 0.000 claims description 2
- 238000002425 crystallisation Methods 0.000 claims description 2
- 238000006386 neutralization reaction Methods 0.000 claims description 2
- NIXOWILDQLNWCW-UHFFFAOYSA-N acrylic acid group Chemical group C(C=C)(=O)O NIXOWILDQLNWCW-UHFFFAOYSA-N 0.000 abstract 1
- 230000001172 regenerating effect Effects 0.000 abstract 1
- 239000002699 waste material Substances 0.000 abstract 1
- UFWIBTONFRDIAS-UHFFFAOYSA-N Naphthalene Chemical compound C1=CC=CC2=CC=CC=C21 UFWIBTONFRDIAS-UHFFFAOYSA-N 0.000 description 12
- YZMHQCWXYHARLS-UHFFFAOYSA-N naphthalene-1,2-disulfonic acid Chemical compound C1=CC=CC2=C(S(O)(=O)=O)C(S(=O)(=O)O)=CC=C21 YZMHQCWXYHARLS-UHFFFAOYSA-N 0.000 description 3
- 239000012847 fine chemical Substances 0.000 description 2
- 239000002994 raw material Substances 0.000 description 2
- GEHJYWRUCIMESM-UHFFFAOYSA-L sodium sulfite Chemical compound [Na+].[Na+].[O-]S([O-])=O GEHJYWRUCIMESM-UHFFFAOYSA-L 0.000 description 2
- 239000004925 Acrylic resin Substances 0.000 description 1
- 229920000178 Acrylic resin Polymers 0.000 description 1
- 230000000274 adsorptive effect Effects 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 230000004927 fusion Effects 0.000 description 1
- 239000011521 glass Substances 0.000 description 1
- 229910017053 inorganic salt Inorganic materials 0.000 description 1
- 238000004064 recycling Methods 0.000 description 1
- 239000012492 regenerant Substances 0.000 description 1
- 230000001105 regulatory effect Effects 0.000 description 1
- 239000002594 sorbent Substances 0.000 description 1
- 238000006277 sulfonation reaction Methods 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
Landscapes
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
- Water Treatment By Sorption (AREA)
- Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)
Abstract
The process of separating and recovering 2-naphthalene sulfonic acid from 2-naphthol producing effluent includes filtering the effluent and adsorbing in fixed bed adsorption column with macroporous acrylic adsorption resin for 2-naphthalene sulfonic acid in the effluent to be adsorbed onto the resin; regenerating the adsorbed resin with hot water or sodium hydroxide solution for reuse and returning the desorbed 2-naphthalene sulfonic acid to the production process for producing 2-naphthol. The said process can recover over 95 % of 2-naphthalene sulfonic acid from 2-naphthol producing effluent, obtain recovered 2-naphthalene sulfonic acid of purity higher than 95 % and lower the CODcr of the effluent from about 40000mg/L to about 20000mg/L, so as to treat effluent while utilizing waste resource.
Description
Technical field
The present invention relates to the pre-treatment of fine chemicals beta naphthal factory effluent, particularly, is to adopt 2-naphthene sulfonic acid in the acrylic resin sorbent material selective adsorption waste water, makes it to obtain Separation and Recovery, makes waste water COD c simultaneously
rA kind of resource utilization pretreatment process that is reduced.
Background technology
Beta naphthal is a kind of important fine chemicals intermediate, and domestic production technique is to be that raw material makes through operations such as sulfonation, alkali fusions with the refined naphthalene at present, will discharge a large amount of high concentrated organic wastewaters in process of production.Waste water COD c
rBe about 40000mg/L, pH is 6～7, mainly contains the 2-naphthene sulfonic acid of 8000～10000mg/L, the 1-naphthalene sulfonic aicd of 3000～4000mg/L, naphthalene disulfonic acid and about 10% S-WAT of 2500～3500mg/L, and a small amount of beta naphthal and naphthalene.Owing to contain the intermediate raw material 2-naphthene sulfonic acid of a large amount of production beta naphthals in this waste water, if can Separation and Recovery, then can not only bring tangible economic benefit, and can effectively reduce the processing load of waste water, for the processing up to standard of the degree of depth of this waste water creates good conditions to manufacturer.
Summary of the invention
The resource utilization pretreatment process that the purpose of this invention is to provide a kind of beta naphthal factory effluent, i.e. 2-naphthene sulfonic acid more than 95% in the Separation and Recovery waste water makes the CODc of waste water simultaneously
rValue is reduced to below the 20000mg/L from about 40000mg/L, realizes the unification of waste water treatment and resource recycling.
Technical scheme of the present invention is as follows:
The method of 2-naphthene sulfonic acid in a kind of Separation and Recovery beta naphthal factory effluent, it is made up of the following step basically:
Step 1. pre-treatment: the beta naphthal factory effluent is handled after filtration, with naphthalene and other suspended matters of removing the waste water surface;
Step 2. absorption: will be by being filled with the ADSORPTION IN A FIXED BED post of macroporous acrylic ester class polymeric adsorbent at 10 ℃～40 ℃ under 0.5～3BV/h (BV is a resin volume in the fixed bed) condition with flow velocity through pretreated factory effluent, the 2-naphthene sulfonic acid is adsorbed on the resin by selectivity, other organism and inorganic salt S-WAT pass through the resin absorption post with waste water substantially, 2-naphthene sulfonic acid content is reduced to below the 50mg/L CODc in the absorption effluent
rReduce to below the 20000mg/L;
Step 3. flushing: with selective adsorption in the step 2 resin of 2-naphthene sulfonic acid in the waste water, water (water temperature＜35 ℃) washes, to remove the residual waste water in resin duct;
Step 4. desorption: resin in the step 3 is carried out desorption and regeneration with desorbing agent, and the desorbing agent flow velocity is 0.5～2BV/h, and desorbing agent can be 65～80 ℃ a hot water, and the concentration that also can be 40～55 ℃ is 1～6%NaOH solution, preferably 65～80 ℃ hot water
Step 5. reclaims: add 30%NaOH solution in step 4 desorption liquid, make pH＞13, the neutralization of 2-naphthene sulfonic acid is cooled to 25～30 ℃ of crystallisation by cooling for the 2-sodium naphthalene sulfonate, and filtered and recycled gets 2-sodium naphthalene sulfonate crystal.
Macroporous acrylic ester class polymeric adsorbent in the above-mentioned steps 2 can be a home-made NDA-7 resin, or the Amberlite XAD-7 resin of the U.S., or the Diaion HP2MG resin of Japan, preferably NDA-7 resin.
Characteristics of the present invention are when handling the beta naphthal factory effluent, can optionally the 2-naphthene sulfonic acid be adsorbed on the resin purity height of the 2-naphthene sulfonic acid of recovery.Adopt the inventive method, the 2-naphthene sulfonic acid in the waste water 95% or more to obtain reclaiming, regenerant purity is substantially devoid of 1-naphthalene sulfonic aicd and naphthalene disulfonic acid greater than 95%, and the CODcr of while waste water reduces to below the 20000mg/L about by 40000mg/L.
Embodiment
Further specify the present invention by the following examples.
The CODcr that produces the raw wastewater of beta naphthal once among the embodiment is 38800mg/L, and pH is 6.5, and the concentration of 2-naphthene sulfonic acid is 8200mg/L, and the concentration of 1-naphthalene sulfonic aicd is 3460mg/L, and the concentration of naphthalene disulfonic acid is 2870mg/L.
Embodiment 1:
(Φ 30 * 250mm), will pass through resin bed with the flow velocity of 5mL/h through the beta naphthal factory effluent of filtering 100mL under the room temperature 1.1 10mL NDA-7 resin is packed in the glass adsorption column of strap clamp cover.The concentration of the 2-naphthene sulfonic acid of absorption effluent is 43mg/L, and CODcr reduces to 18700mg/L.
1.2 wash adsorbing the back resin with 20ml, about 25～30 ℃ water, remove residual waste water in the resin duct.
1.3 with 80 ℃ hot water with the 5mL/h flow velocity by the flushing after resin, resin is carried out desorption and regeneration, desorption liquid is regulated pH＞13 with 30%NaOH, is cooled to 25 ℃, filtered and recycled purity reaches 96% 2-sodium naphthalene sulfonate 783mg.Recover adsorptive power through eluted resins.
Embodiment 2: step is with embodiment 1, but the waste water of step 1 is passed through resin bed with the flow velocity of 30mL/h; 80 ℃ hot water in the step 1.3 with the 5mL/h flow velocity by the flushing after resin use instead 65 ℃ hot water with the 20mL/h flow velocity by the flushing after resin, other conditions are constant, except that every batch of adsorption treatment amount changed, its result was identical with embodiment 1.
Embodiment 3:
Step is with embodiment 1, changes the desorbing agent hot water in the step 1.3 into 55 ℃, 1% NaOH solution, and other conditions remain unchanged, and its result of implementation is basic identical with embodiment 1.
Embodiment 4:
Step is with embodiment 1, changes the desorbing agent hot water in the step 1.3 into 40 ℃, 6% NaOH solution, and other conditions remain unchanged, and its result of implementation is basic identical with embodiment 1.
Embodiment 5:
Step changes NDA-7 resin in the step 1.1 into Amberlite XAD-7 resin with embodiment 1, DiaionHP2MG resin perhaps, and other conditions remain unchanged, and except that every batch processed amount changed, other result of implementation and embodiment 1 were suitable substantially.
Claims (4)
1. the method for 2-naphthene sulfonic acid in the Separation and Recovery beta naphthal factory effluent is characterized in that it is made up of the following step basically:
Step 1. pre-treatment: the beta naphthal factory effluent is handled after filtration;
Step 2. absorption: will be by being filled with the ADSORPTION IN A FIXED BED post of macroporous acrylic ester class polymeric adsorbent at 10 ℃～40 ℃ under 0.5～3BV/h condition with flow velocity through pretreated factory effluent;
Step 3. flushing: with selective adsorption in the step 2 resin of 2-naphthene sulfonic acid in the waste water, wash the residual waste water in removal resin duct with the water of water temperature＜35 ℃;
Step 4. desorption: resin in the step 3 is carried out desorption and regeneration with desorbing agent, and the desorbing agent flow velocity is 0.5～2BV/h, and desorbing agent is 65～80 ℃ a hot water, or 40～55 ℃ concentration is 1～6%NaOH solution;
Step 5. reclaims: add 30%NaOH solution in step 4 desorption liquid, make pH＞13, the neutralization of 2-naphthene sulfonic acid is cooled to 25～30 ℃ of crystallisation by cooling for the 2-sodium naphthalene sulfonate, and filtered and recycled gets 2-sodium naphthalene sulfonate crystal.
2. method according to claim 1 is characterized in that: the macroporous acrylic ester class polymeric adsorbent in the described step 2 is a home-made NDA-7 resin, or the Amberlite XAD-7 resin of the U.S., or the DiaionHP2MG resin of Japan.
3. method according to claim 2 is characterized in that: the macroporous acrylic ester class polymeric adsorbent in the described step 2 is the NDA-7 resin.
4. method according to claim 1 is characterized in that: the desorbing agent in the described step 4 is 65～80 ℃ a hot water.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CNB2006100884900A CN100360498C (en) | 2006-08-25 | 2006-08-25 | Method of separating and recovering 2-naphthalenesulfonic acid from waste water of 2-naphthol production |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CNB2006100884900A CN100360498C (en) | 2006-08-25 | 2006-08-25 | Method of separating and recovering 2-naphthalenesulfonic acid from waste water of 2-naphthol production |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN1911906A true CN1911906A (en) | 2007-02-14 |
| CN100360498C CN100360498C (en) | 2008-01-09 |
Family
ID=37720998
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CNB2006100884900A Active CN100360498C (en) | 2006-08-25 | 2006-08-25 | Method of separating and recovering 2-naphthalenesulfonic acid from waste water of 2-naphthol production |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN100360498C (en) |
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102838232A (en) * | 2012-09-03 | 2012-12-26 | 济宁阳光煤化有限公司 | Process for processing 2-sodium naphthalene sulfonate mother liquor by blowing and resin absorption |
| CN102936054A (en) * | 2011-12-30 | 2013-02-20 | 滨州学院 | Method for separating naphthalene sulfonic acid, sulfuric acid and sulfurous acid from industrial wastewater |
| CN102963960A (en) * | 2012-12-21 | 2013-03-13 | 南京大学 | Method for simultaneously recycling sulfuric acid and organic substances in m-cresol production wastewater |
| CN105948294A (en) * | 2016-06-16 | 2016-09-21 | 山东同源和环境工程有限公司 | Waste acid resourceful treatment process based on nano-composite carrier retarding method |
Family Cites Families (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1139539C (en) * | 2001-07-18 | 2004-02-25 | 南京大学 | Method of treating naphthalene-blowing effluence and recovering resource in 2-naphthol producing process |
| CN1323041C (en) * | 2005-07-05 | 2007-06-27 | 南京大学 | Waste water treating and resourcelization method for tobias acid production |
-
2006
- 2006-08-25 CN CNB2006100884900A patent/CN100360498C/en active Active
Cited By (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102936054A (en) * | 2011-12-30 | 2013-02-20 | 滨州学院 | Method for separating naphthalene sulfonic acid, sulfuric acid and sulfurous acid from industrial wastewater |
| CN102838232A (en) * | 2012-09-03 | 2012-12-26 | 济宁阳光煤化有限公司 | Process for processing 2-sodium naphthalene sulfonate mother liquor by blowing and resin absorption |
| CN102838232B (en) * | 2012-09-03 | 2013-09-11 | 济宁阳光煤化有限公司 | Process for processing 2-sodium naphthalene sulfonate mother liquor by blowing and resin absorption |
| CN102963960A (en) * | 2012-12-21 | 2013-03-13 | 南京大学 | Method for simultaneously recycling sulfuric acid and organic substances in m-cresol production wastewater |
| CN102963960B (en) * | 2012-12-21 | 2014-07-16 | 南京大学 | Method for simultaneously recycling sulfuric acid and organic substances in m-cresol production wastewater |
| CN105948294A (en) * | 2016-06-16 | 2016-09-21 | 山东同源和环境工程有限公司 | Waste acid resourceful treatment process based on nano-composite carrier retarding method |
| CN105948294B (en) * | 2016-06-16 | 2018-08-17 | 山东同源和环境工程有限公司 | A kind of waste acid resource treatment process blocking method based on nano combined carrier |
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| Publication number | Publication date |
|---|---|
| CN100360498C (en) | 2008-01-09 |
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Address after: 210093 Hankou Road, Jiangsu, China, No. 22, No. Co-patentee after: Jiangsu N&J Environmental Technology Co., Ltd. Patentee after: Nanjing University Address before: 210093 Hankou Road, Jiangsu, China, No. 22, No. Co-patentee before: Jiangsu NJU Gede Environmental Protection Technology Co., Ltd. Patentee before: Nanjing University |
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| CP01 | Change in the name or title of a patent holder | ||
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Address after: 210093 No. 22, Hankou Road, Nanjing, Jiangsu Co-patentee after: Jiangsu NJU Environmental Technology Co., Ltd. Patentee after: Nanjing University Address before: 210093 No. 22, Hankou Road, Nanjing, Jiangsu Co-patentee before: Jiangsu N&J Environmental Technology Co., Ltd. Patentee before: Nanjing University |