CN1258555A - Double filter layer filtering bed process for treating printing and dyeing effluents - Google Patents
Double filter layer filtering bed process for treating printing and dyeing effluents Download PDFInfo
- Publication number
- CN1258555A CN1258555A CN 99120641 CN99120641A CN1258555A CN 1258555 A CN1258555 A CN 1258555A CN 99120641 CN99120641 CN 99120641 CN 99120641 A CN99120641 A CN 99120641A CN 1258555 A CN1258555 A CN 1258555A
- Authority
- CN
- China
- Prior art keywords
- layer
- filter bed
- waste water
- dyeing
- filter
- 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
Images
Landscapes
- Separation Of Suspended Particles By Flocculating Agents (AREA)
- Removal Of Specific Substances (AREA)
- Treatment Of Water By Oxidation Or Reduction (AREA)
Abstract
The present invention relates to the treatment of waste water. The filtering bed consists of two layers, an iron-carbon layer and a calcium hydroxide layer. It treats printing and dyeing effluents at normal temperature and pressure without adding any chemical and at the rate of 400-500 1/sq m.hr and can result in a decolorizing rate of 70-90%, a COD eliminating rate greater than 50% and low treatment cost. The present invention is suitable for application in industrial scale.
Description
The present invention relates to the method for a kind of pair of filtering layer filter bed treatment of dyeing and printing, belong to technical field of sewage.
At present, domestic employing filter method treatment of dyeing and printing is concluded and is got up to have following three kinds, and the one, membrane filtration, the 2nd, millipore filtration, the 3rd, bed of iron filings is filtered.The dyeing waste water water yield is big, and the component content complexity changes greatly, and above-mentioned three kinds of treatment processs all have many problems and difficulty on large-scale application.The method that has is little and impracticable because of treatment capacity, rests on experimental stage for a long time.The method that has can be carried out behind the medicaments such as PFS because of adding flocculation agent such as PAC, has increased processing cost, can not compete with the air supporting method.It is a kind of method of utilizing the microelectrolyzing iron filings to obtain principle that waste water is handled that bed of iron filings is filtered, and decolorizing effect is good, but to the clearance of COD generally about 20%.From the iron filings fixed bed that puts into operation at present, only to handle the dye well Intermediate Wastewater, the large-scale application on treatment of dyeing wastewater is not reported.
Develop a kind of treatment of dyeing and printing in a large number, do not need to add the filter bed that flocculation agent is handled again, meaning is very big.The objective of the invention is to propose the method for a kind of pair of filtering layer filter bed treatment of dyeing and printing, for the large-scale application of filter bed treatment of dyeing and printing creates conditions.
Content of the present invention is: the organigram of two filtering layer filter beds as shown in drawings, leave the space of high 10~25cm at iron filter vat 1 trench bottom, put filtrate outlet 7 at downside, and valve is housed regulates the filtrate flow, also be equipped with the blow-down pipe 8 of a band cock in this spatial side, to keep atmospheric operation, in groove, deploy card or web plate, put double-deck filtering layer on this card or web plate, the filtering layer A of lower floor layer 2 is made of the mixture of cast iron filing and wood charcoal powder, is laid on the filter cloth, thickness is 2~8cm, upper strata filtering layer B layer 3 is made of the calcium hydroxide white particle, is laid on another filter cloth, and thickness is 0.3~0.5cm, the B metafiltration is placed on the A metafiltration layer, the centre is separated by by filter cloth, and groove top maintains the dyeing waste water submergence on B metafiltration layer, liquid level 4 height 1~5cm, shower 5 is housed on groove, the spray dyeing waste water, shower is equipped with into water valve 6, regulates the dyeing waste water filtration yield.
The making of filter bed:
1, required starting material
Cast iron filing: the nodular iron casting cutting belongs to proportion 7.0, silver gray or beige, non-corrosive, granularity 50~60 orders.
Wood charcoal powder: commercially available.About proportion 1.1, do not contain things such as earth, weeds, granularity 40~50 orders.
Milk of lime: self-control.Adding clear water with unslaked lime makes.
95% sulfuric acid: commercially available.Technical grade.
Filter cloth: commercially available.Industrial chemical fibre filter cloth.
2, the making of filtering layer
A layer: cast iron filing and wood charcoal powder are mixed by 1: 1~1.5 volume ratios (amount to weight ratio be about 1: 0.15~0.25), drop in the dilution heat of sulfuric acid of 3~5% concentration, soaked 1~2 hour, pull out then and evenly be laid on the off-the-shelf industrial filter cloth.
The B layer: milk of lime is added the clear water washing, and to solution pH value about 7, the supernatant liquor that inclines evenly is laid on the calcium hydroxide white particulate material that stays on the off-the-shelf industrial filter cloth.
3, filter bed is made
Earlier filter cloth is laid on the card or web plate of filter vat, evenly lays A metafiltration material then, thickness is 2~8cm, and B metafiltration cloth is laid on above the A metafiltration material, evenly lays B metafiltration material then, and thickness is 0.3~0.5cm.
The technological process of treatment of dyeing and printing: dyeing waste water is transferred pH value to 5~5.5 with sulfuric acid, enter filter bed with certain flow then, when handling operation, open the blow-down pipe cock, make the maintenance normal pressure, open bottom filtrate outlet valve, make filter vat bottom space liquid keep emptying, regulate shower dyeing waste water water inlet valve, maintain the dyeing waste water submergence above being controlled at B metafiltration layer, liquid level 1~5cm is handling operation during intermittence, close filtrate outlet valve earlier, trench bottom to be filtered space is full of waste water, and after being overflowed by the blow-down pipe cock, promptly closes the blow-down pipe cock, close the influent waste water valve then, make filter bed keep being immersed in the waste water.Repeat when operating next time.Waste water filter amount was advisable with 400~500 liters/square metre hours.The diameter of filter vat can be designed as 1.5~3 meters and is advisable.Filtrate is transferred pH value 6~7 with milk of lime again, coagulative precipitation, and whole technological process is finished at normal temperatures and pressures.
Advantage of the present invention is: described filter bed is easy to make, and raw material is easy to get, and is cheap, and operating maintenance is easy; Can handle the dyeing waste water of various concentration, effect is remarkable, percent of decolourization 70~90%, COD
CrClearance 〉=50% is saved processing costs 20~30%.Meaning of the present invention is: the one, realized that at normal temperatures and pressures dyeing waste water being carried out materialization handles, and need not add medicaments such as flocculation agent and discoloring agent, and China produces about 3,000,000 tons of dyeing waste waters every day at present, the annual medicament that consumes, expense is up to several hundred million units.It two is can be according to the size of dyeing waste water amount, design and produce a kind of multistage pair of filtering layer column plate type filter bed and carry out the parallel connection processing, realize the heavy industrialization application of filter bed treatment of dyeing and printing, treatment capacity is big, overcomes present iron filings fixed bed and handles the little shortcoming of wastewater flow rate.It three is that filtrate after the filtration treatment is suitable for further doing biochemical treatment.Also have, the filter bed that the present invention uses, the water inlet pH value is 5~5.5, and the requirement of iron filings fixed bed water inlet pH value is 1~2, thereby the consumption of iron filings is much smaller among the present invention.Adopt double-deck filtering layer can also reduce the obstruction of dying the confrontation filtering layer in the waste water, and operation keeps the submergence of waste water to filter bed intermittently the time, all prolong filter bed work-ing life greatly.To sum up, the inventive method is that a kind of treatment effect is good, and equipment life is long, convenient operation and management, the novel water treatment method that running cost is low has fairly obvious economic benefit, social environment benefit meets the requirement of the national economic development strategy of sustainable development fully.
Embodiment 1:
Dyeing waste water is from Changshu City first and second printing and dyeing mills of company, and chemical fibre dyeing is main, and active, dispersed dye are main.Add sulfuric acid and transfer waste water pH value to 5.2, waste water COD
Cr934mg/1,120 times of colourities, beige.A metafiltration material thickness 5cm, B metafiltration material thickness 0.5cm, liquid level 4~5cm, the amount of leaching 400~500 liters/square metre hours.Detected once in per 15 minutes, the result is as follows
???????????COD cr | Colourity | ||
Measured value mg/l | Clearance (%) | Measured value (doubly) | Clearance (%) |
????362 | ????61.2 | ????<20 | ????83 |
????338 | ????63.8 | ????<20 | ????83 |
????275 | ????70.6 | ????<20 | ????83 |
????292 | ????68.7 | ????<20 | ????83 |
Embodiment 2:
Dyeing waste water is from the pool, East Lake, Xishan city Jin Rong woollen mill, and wool spinning dyeing waste-water, matching stain are main.Waste water adds sulfuric acid and transfers PH to 5.1, waste water COD
Cr1950mg/l, 400 times of colourities, blue or green brown.Filter bed and operational condition are with example 1.Detected 1 time in per 15 minutes, detected result is as follows
??????????COD cr | Colourity | ||
Measured value mg/l | Clearance (%) | Measured value (doubly) | Clearance (%) |
????695 | ????64.3 | ??????30 | ?????92.5 |
????745 | ????61.8 | ??????70 | ?????82.5 |
????745 | ????61.8 | ??????50 | ?????87.5 |
????815 | ????58.2 | ??????50 | ?????87.5 |
????795 | ????59.2 | ??????80 | ?????80 |
Embodiment 3:
Dyeing waste water is taken from the Xishan city special wealthy printing and dyeing mill of snow plumage, and piece dyeing finishing contains a large amount of desized wastewaters.Add waste water pH value 5.0 behind the sulfuric acid, COD
Cr6015mg/l, 100 times of colourities, milk yellow.Filter bed and technological operation are with example 1.Took a sample once in per 20 minutes, detected result is as follows.
??????????????COD cr | Colourity | ||
Measured value (mg/l) | Clearance (%) | Measured value (doubly) | Clearance (%) |
????2488 | ????58.6 | ????<20 | ????80 |
????2520 | ????58.1 | ????<20 | ????80 |
????2590 | ????56.9 | ????<20 | ????80 |
????2600 | ????56.7 | ????<20 | ????80 |
Description of drawings: 1 filter vat, the 2 filtering layer A of lower floor layer cast iron filing wood charcoal powder mixing filtering layers, 3 upper strata filtering layer B layer calcium hydroxide filtering layers, the submergence liquid layer on 4B layer top, 5 showers, 6 water intakes, the outlet of 7 filtrates, 8 blow-down pipes.
Claims (4)
1, a kind of method of filter bed treatment of dyeing and printing, feature of the present invention is that filter bed is made up of two-layer different filtering layer, the filtering layer A of lower floor layer is made of the mixture of cast iron filing and wood charcoal powder, upper strata filtering layer B layer is made of the calcium hydroxide white particle, the dyeing waste water that to regulate pH value to 5~5.5 then enters filter bed with the filter amount up to 400~500 liters/square metre hour, decolours and COD
CrRemove technology, the entire operation process is carried out at normal temperatures and pressures, the decolorizing printing and dyeing waste water rate after the processing: 70~90%, and COD
CrClearance 〉=50%; , all should keep filter bed is immersed in the waste water intermittently the time in filtration treatment or operation.
2, in accordance with the method for claim 1, the cast iron filing that it is characterized in that constituting filter bed A layer is the nodular iron casting cutting swarf, proportion 7.0, granularity 50~60 orders; Wood charcoal powder proportion 1.1, granularity are 40~50 orders, and cast iron filing is mixed by 1: 1~1.5 volume ratio proportionings with wood charcoal powder, drop in 3~5% concentration dilute sulfuric acid solutions and soak 1~2 hour, pull out then evenly to be laid on the industrial filter cloth, and thickness of filter bed is 2~8cm.
3, by the described method of claim 1, the calcium hydroxide particle that it is characterized in that constituting filter bed B layer is that milk of lime is washed to solution pH value about 7 with clear water, supernatant liquor inclines, the white particulate material that stays, evenly be laid on the industrial filter cloth, thickness of filter bed is 0.3~0.5cm, and the B metafiltration is placed on the A metafiltration layer, and the centre is separated by by filter cloth.
4, in accordance with the method for claim 1, it is characterized in that entering the dyeing waste water of filter bed earlier with sulfuric acid adjusting pH value to 5~5.5, waste water is filtered by B course A layer, the effusive filtrate of A layer transferred pH value to 6~7 with milk of lime again, coagulative precipitation, the liquid level of dyeing waste water on the B layer keeps 1~5cm in the filter bed.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN 99120641 CN1124169C (en) | 1999-12-17 | 1999-12-17 | Double filter layer filtering bed process for treating printing and dyeing effluents |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN 99120641 CN1124169C (en) | 1999-12-17 | 1999-12-17 | Double filter layer filtering bed process for treating printing and dyeing effluents |
Publications (2)
Publication Number | Publication Date |
---|---|
CN1258555A true CN1258555A (en) | 2000-07-05 |
CN1124169C CN1124169C (en) | 2003-10-15 |
Family
ID=5281608
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN 99120641 Expired - Fee Related CN1124169C (en) | 1999-12-17 | 1999-12-17 | Double filter layer filtering bed process for treating printing and dyeing effluents |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN1124169C (en) |
Cited By (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1329311C (en) * | 2003-11-06 | 2007-08-01 | 徐宝安 | Bearing sewage processor with coal as filtering material |
CN1329310C (en) * | 2003-11-06 | 2007-08-01 | 徐宝安 | Module assembled bearing coal filtering sewage processor |
CN101269898B (en) * | 2008-04-29 | 2010-12-29 | 中国地质大学(武汉) | Advanced treatment apparatus for printing and dyeing wastewater |
CN102531224A (en) * | 2010-12-22 | 2012-07-04 | 常州市环境保护研究所 | Method and device for recovering indigoid dye |
CN104671504A (en) * | 2015-03-01 | 2015-06-03 | 山东黄河三角洲纺织科技研究院有限公司 | Treatment method of alkali boiling-off wastewater of cotton fabrics |
CN105561658A (en) * | 2014-10-14 | 2016-05-11 | 中国石油化工股份有限公司 | Separation and purification equipment and method for melt crystalline suspension |
CN110357322A (en) * | 2019-07-09 | 2019-10-22 | 容健美 | A kind of environment-friendly type printing-dyeing waste water treatment process and processing unit |
-
1999
- 1999-12-17 CN CN 99120641 patent/CN1124169C/en not_active Expired - Fee Related
Cited By (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1329311C (en) * | 2003-11-06 | 2007-08-01 | 徐宝安 | Bearing sewage processor with coal as filtering material |
CN1329310C (en) * | 2003-11-06 | 2007-08-01 | 徐宝安 | Module assembled bearing coal filtering sewage processor |
CN101269898B (en) * | 2008-04-29 | 2010-12-29 | 中国地质大学(武汉) | Advanced treatment apparatus for printing and dyeing wastewater |
CN102531224A (en) * | 2010-12-22 | 2012-07-04 | 常州市环境保护研究所 | Method and device for recovering indigoid dye |
CN102531224B (en) * | 2010-12-22 | 2015-12-02 | 江苏常环环境科技有限公司 | A kind of method that bipseudoindoxyl dye reclaims and device |
CN105561658A (en) * | 2014-10-14 | 2016-05-11 | 中国石油化工股份有限公司 | Separation and purification equipment and method for melt crystalline suspension |
CN105561658B (en) * | 2014-10-14 | 2018-09-14 | 中国石油化工股份有限公司 | Fusion-crystallization suspension isolates and purifies device and method |
CN104671504A (en) * | 2015-03-01 | 2015-06-03 | 山东黄河三角洲纺织科技研究院有限公司 | Treatment method of alkali boiling-off wastewater of cotton fabrics |
CN110357322A (en) * | 2019-07-09 | 2019-10-22 | 容健美 | A kind of environment-friendly type printing-dyeing waste water treatment process and processing unit |
Also Published As
Publication number | Publication date |
---|---|
CN1124169C (en) | 2003-10-15 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN100457645C (en) | Zero discharge and circular utilization method of industrial effluent in regeneration treatment | |
CN203247146U (en) | Ecological earthworm filtering pool with effective denitrification function | |
CN209242891U (en) | A kind of sludge dewatering treatment system | |
Middlebrooks et al. | Techniques for algae removal from wastewater stabilization ponds | |
CN1124169C (en) | Double filter layer filtering bed process for treating printing and dyeing effluents | |
Schulz et al. | Treating surface waters for communities in developing countries | |
CN214299633U (en) | Backwashing wastewater treatment device for denitrification deep bed filter | |
CN201485349U (en) | Dynamic circulating water treater | |
CN212174750U (en) | Dye printing wastewater purification treatment system | |
CN201125201Y (en) | Combined type intermediate water treating eqiupment | |
Meenakshipriya et al. | Study of pH system in common effluent treatment plant | |
CN105060626B (en) | A kind of processing method of papermaking factory production waste water | |
CN104986924B (en) | A kind of processing system of papermaking factory production waste water | |
CN211170300U (en) | Ultra-low pressure gravity-driven biological ultrafiltration coupling water purification device | |
CN105198163B (en) | A kind of WASTEWATER TREATMENT OF FOOD PROCESSING INDUSTRY system and method | |
CN209797719U (en) | Take sewage treatment system of fiber ball filter back flush | |
CN107840536A (en) | Integrated form integration ecological water factory | |
CN1673119A (en) | Biological purifying process of seriously polluted river water | |
CN113998845A (en) | Water body ecological restoration system | |
CN208949091U (en) | A kind of total system of textile manufacturing waste water | |
CN208869428U (en) | A kind of waste water dephosphorization equipment for reclaiming | |
KR20110058929A (en) | Integrated method for treating food waste water, livestock waste water, and night soil | |
CN208087361U (en) | A kind of Water Treatment equipment | |
CN207641130U (en) | A kind of device handling country sewage using filtrate | |
Kumar et al. | Recycling of woven fabric dyeing wastewater practiced in Perundurai common effluent treatment plant |
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 | ||
C19 | Lapse of patent right due to non-payment of the annual fee | ||
CF01 | Termination of patent right due to non-payment of annual fee |