CN104086043B - A kind for the treatment of of dyeing wastewater reuse method - Google Patents
A kind for the treatment of of dyeing wastewater reuse method Download PDFInfo
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- CN104086043B CN104086043B CN201410283756.1A CN201410283756A CN104086043B CN 104086043 B CN104086043 B CN 104086043B CN 201410283756 A CN201410283756 A CN 201410283756A CN 104086043 B CN104086043 B CN 104086043B
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- 239000002351 wastewater Substances 0.000 title claims abstract description 31
- 238000000034 method Methods 0.000 title claims abstract description 29
- 238000004043 dyeing Methods 0.000 title claims abstract description 16
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 53
- 230000003647 oxidation Effects 0.000 claims abstract description 15
- 238000007254 oxidation reaction Methods 0.000 claims abstract description 15
- 239000000463 material Substances 0.000 claims abstract description 12
- 230000007062 hydrolysis Effects 0.000 claims abstract description 7
- 238000006460 hydrolysis reaction Methods 0.000 claims abstract description 7
- 230000020477 pH reduction Effects 0.000 claims abstract description 7
- 238000005342 ion exchange Methods 0.000 claims abstract description 6
- 238000001556 precipitation Methods 0.000 claims abstract description 4
- 238000001914 filtration Methods 0.000 claims description 8
- 239000002244 precipitate Substances 0.000 claims description 8
- 238000005188 flotation Methods 0.000 claims description 6
- 230000001105 regulatory effect Effects 0.000 claims description 6
- 238000004062 sedimentation Methods 0.000 claims description 6
- 239000005416 organic matter Substances 0.000 claims description 5
- 239000006228 supernatant Substances 0.000 claims description 5
- 238000004519 manufacturing process Methods 0.000 claims description 4
- -1 and afterwards Substances 0.000 claims description 3
- 238000004061 bleaching Methods 0.000 claims description 3
- 239000007844 bleaching agent Substances 0.000 claims description 3
- 238000007664 blowing Methods 0.000 claims description 3
- 238000004042 decolorization Methods 0.000 claims description 3
- 230000003301 hydrolyzing effect Effects 0.000 claims description 3
- 230000007704 transition Effects 0.000 claims description 3
- 238000003912 environmental pollution Methods 0.000 abstract description 4
- 230000000694 effects Effects 0.000 abstract description 3
- 238000004064 recycling Methods 0.000 abstract description 3
- 230000036642 wellbeing Effects 0.000 abstract description 3
- 238000000926 separation method Methods 0.000 abstract 1
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 4
- 238000005516 engineering process Methods 0.000 description 3
- 229910052757 nitrogen Inorganic materials 0.000 description 2
- 239000002245 particle Substances 0.000 description 2
- 238000000247 postprecipitation Methods 0.000 description 2
- 239000007787 solid Substances 0.000 description 2
- 239000000725 suspension Substances 0.000 description 2
- 238000000108 ultra-filtration Methods 0.000 description 2
- 238000004065 wastewater treatment Methods 0.000 description 2
- 230000009286 beneficial effect Effects 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 239000010842 industrial wastewater Substances 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 238000009970 yarn dyeing Methods 0.000 description 1
Landscapes
- Treatment Of Water By Oxidation Or Reduction (AREA)
- Treatment Of Water By Ion Exchange (AREA)
- Biological Treatment Of Waste Water (AREA)
- Separation Using Semi-Permeable Membranes (AREA)
Abstract
The invention provides a kind for the treatment of of dyeing wastewater reuse method, its key step is: 1. all with the water yield and water quality, 2. hydrolysis acidification, 3. biological contact oxidation pond processing, 4. precipitation, 5. BAF processing, 6. pottery material filters 7. milipore filters separation, 8. ion exchange system processing; Whole method is more excellent than former mode treatment effect, can and re-use, and only produce and even do not produce on a small quantity discharge of wastewater in rivers through the water of this kind of method processing, has realized recycling of water, has reduced environmental pollution, promotes the well-being of mankind.
Description
Technical field
The present invention relates to the field of waste water treatment of yarn dyeing, relate in particular to a kind for the treatment of of dyeing wastewater reuse method.
Background technology
Dyeing waste water belongs in industrial wastewater compared with the one of refractory reason. Due to technology, economic dispatch reason, biology-physics improvement method that most adopts can only reach basic emission request. Although slightly decline in colourity, organic substance is just resolved into less material, these catabolite character are difficult to control also very difficult grasp, cannot ensure environment not produce harm. Existing wastewater treatment mode ability can not meet present situation or need of production in the future soon, along with the attention of country to energy-saving and emission-reduction and environmental pollution, for our offspring, how to ensure the minimizing discharge of dyeing waste water or do not discharge just to seem very necessary.
Summary of the invention
For existing deficiency, the object of this invention is to provide a kind for the treatment of of dyeing wastewater reuse method, adopt biological contact oxidation pond, a secondary BAF to carry out advanced treating, after processing, expect to filter by pottery again and separate with milipore filter, the water obtaining can utilize again, has solved the problem occurring in background technology.
The object of this invention is to provide a kind for the treatment of of dyeing wastewater reuse method, comprise the following steps:
Step 1: dyeing waste water is discharged in regulating reservoir all and its water yield and water quality, and the water of regulating reservoir enters in hydrolysis acidification pool and processes;
Step 2: the water in hydrolysis acidification pool is discharged in biological contact oxidation pond and carries out denitrogenation removal organic matter, and afterwards, waste water is discharged in sedimentation basin and precipitates and add bleaching agent bleaching, and the complete waste water of precipitate and decolorization enters in flotation tank;
Step 3: the precipitation of sedimentation basin is discharged in sludge-tank, sludge-tank supernatant is discharged in hydrolytic tank to be processed again, and after the mud in sludge-tank carries out press filtration, outward transport is processed;
Step 4: the water in flotation tank enters into the transition of intermediate pool I, enters into afterwards in BAF and further carries out biochemical treatment, and the water being disposed enters into intermediate pool II;
Step 5: the material filter of making pottery successively of the water in intermediate pool II filters and carries out film with milipore filter and separate, be discharged to afterwards in clear water reserviors stand-by, in the time preparing to use the water in clear water reserviors, line that it just can be put into production after ion-exchange treatment system is processed uses.
Further improve and be: the BAF in biological contact oxidation pond and step 4 in described step 2 all needs by air blast blowing is set.
Further improve and be: in described step 5, pottery material filter and milipore filter carry out backwash to it in the time filtering interval.
Further improve and be: in described step 2, biological contact oxidation pond is provided with at least 4 in parallel uses, in step 3, BAF is provided with at least 2 in parallel uses.
Beneficial effect of the present invention: this method first through all with its water yield and water quality, then the acidifying that is hydrolyzed improves to be convenient to carry out a biological contact oxidation pond after the biodegradability of waste water and to process and remove nitrogen and organic matter, precipitate afterwards and remove mud, supernatant in mud can be proceeded to process again, reduce the discharge of water, the waste water of having removed mud carries out secondary BAF and further carries out biochemical treatment, effectively reduce the residual COD in water, integrate biological oxidation and hold back suspended solid, save post precipitation pond (second pond), the waste water of secondary biological treatment is filtering and is separating the suspension and the particle that further filter out in water with milipore filter through pottery material, filter at pottery material the gap separating with ultra filtration it is carried out to backwash, effectively avoid its putty, treated water enters clear water reserviors and processes and just can directly use through ion exchange system before use, whole method is more excellent than former mode treatment effect, water through this kind of method processing can and re-use, and only produce and even do not produce on a small quantity discharge of wastewater in rivers, realize recycling of water, reduce environmental pollution, promote the well-being of mankind.
Detailed description of the invention
In order to deepen the understanding of the present invention, below in conjunction with embodiment, the invention will be further described, and this embodiment only, for explaining the present invention, does not form limiting the scope of the present invention.
The present embodiment provides a kind for the treatment of of dyeing wastewater reuse method, comprises the following steps:
Step 1: dyeing waste water is discharged in regulating reservoir all and its water yield and water quality, and the water of regulating reservoir enters in hydrolysis acidification pool and processes;
Step 2: the water in hydrolysis acidification pool is discharged in biological contact oxidation pond and carries out denitrogenation removal organic matter, and afterwards, waste water is discharged in sedimentation basin and precipitates and add bleaching agent bleaching, and the complete waste water of precipitate and decolorization enters in flotation tank;
Step 3: the precipitation of sedimentation basin is discharged in sludge-tank, sludge-tank supernatant is discharged in hydrolytic tank to be processed again, and after the mud in sludge-tank carries out press filtration, outward transport is processed;
Step 4: the water in flotation tank enters into the transition of intermediate pool I, enters into afterwards in BAF and further carries out biochemical treatment, and the water being disposed enters into intermediate pool II;
Step 5: the material filter of making pottery successively of the water in intermediate pool II filters and carries out film with milipore filter and separate, be discharged to afterwards in clear water reserviors stand-by, in the time preparing to use the water in clear water reserviors, line that it just can be put into production after ion-exchange treatment system is processed uses.
BAF in biological contact oxidation pond and step 4 in step 2 all needs by air blast blowing is set; In step 5, pottery material filter and milipore filter carry out backwash to it in the time filtering interval; In described step 2, biological contact oxidation pond is provided with 4 in parallel uses, and in step 3, BAF is provided with 2 in parallel uses.
This method first through all with its water yield and water quality, then the acidifying that is hydrolyzed improves to be convenient to carry out a biological contact oxidation pond after the biodegradability of waste water and to process and remove nitrogen and organic matter, precipitate afterwards and remove mud, supernatant in mud can be proceeded to process again, reduce the discharge of water, the waste water of having removed mud carries out secondary BAF and further carries out biochemical treatment, effectively reduce the residual COD in water, integrate biological oxidation and hold back suspended solid, save post precipitation pond (second pond), the waste water of secondary biological treatment is filtering and is separating the suspension and the particle that further filter out in water with milipore filter through pottery material, filter at pottery material the gap separating with ultra filtration it is carried out to backwash, effectively avoid its putty, treated water enters clear water reserviors and processes and just can directly use through ion exchange system before use, whole method is more excellent than former mode treatment effect, water through this kind of method processing can and re-use, and only produce and even do not produce on a small quantity discharge of wastewater in rivers, realize recycling of water, reduce environmental pollution, promote the well-being of mankind.
Claims (4)
1. a treatment of dyeing wastewater reuse method, is characterized in that: comprise the following steps:
Step 1: dyeing waste water is discharged in regulating reservoir all and its water yield and water quality, and the water of regulating reservoir enters in hydrolysis acidification pool and processes;
Step 2: the water in hydrolysis acidification pool is discharged in biological contact oxidation pond and carries out denitrogenation removal organic matter, and afterwards, waste water is discharged in sedimentation basin and precipitates and add bleaching agent bleaching, and the complete waste water of precipitate and decolorization enters in flotation tank;
Step 3: the precipitation of sedimentation basin is discharged in sludge-tank, sludge-tank supernatant is discharged in hydrolytic tank to be processed again, and after the mud in sludge-tank carries out press filtration, outward transport is processed;
Step 4: the water in flotation tank enters into the transition of intermediate pool I, enters into afterwards in BAF and further carries out biochemical treatment, and the water being disposed enters into intermediate pool II;
Step 5: the material filter of making pottery successively of the water in intermediate pool II filters and carries out film with milipore filter and separate, be discharged to afterwards in clear water reserviors stand-by, in the time preparing to use the water in clear water reserviors, line that it just can be put into production after ion-exchange treatment system is processed uses.
2. a kind for the treatment of of dyeing wastewater reuse method as claimed in claim 1, is characterized in that: the BAF in biological contact oxidation pond and step 4 in described step 2 all needs by air blast blowing is set.
3. a kind for the treatment of of dyeing wastewater reuse method as claimed in claim 1, is characterized in that: in described step 5, pottery material filter and milipore filter carry out backwash to it in the time filtering interval.
4. a kind for the treatment of of dyeing wastewater reuse method as claimed in claim 1, is characterized in that: in described step 2, biological contact oxidation pond is provided with at least 4 in parallel uses, and in step 3, BAF is provided with at least 2 in parallel uses.
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CN201410283756.1A CN104086043B (en) | 2014-06-24 | 2014-06-24 | A kind for the treatment of of dyeing wastewater reuse method |
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CN201410283756.1A CN104086043B (en) | 2014-06-24 | 2014-06-24 | A kind for the treatment of of dyeing wastewater reuse method |
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CN104086043B true CN104086043B (en) | 2016-05-25 |
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CN106045023A (en) * | 2016-07-31 | 2016-10-26 | 深圳市深联众诚环保技术工程有限公司 | System and method for sewage treatment |
CN107365014A (en) * | 2017-06-29 | 2017-11-21 | 芜湖富春染织股份有限公司 | A kind of method for reclaiming waste water of yarn dip-dye liquid |
CN107352740A (en) * | 2017-07-27 | 2017-11-17 | 张家港市双盈印染有限公司 | A kind of printing and dyeing waste water advanced treatment recovery method |
Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101070216A (en) * | 2007-06-18 | 2007-11-14 | 华南理工大学 | Integrated ozone and aeration biological filtering pool water treatment apparatus and method |
CN101234814A (en) * | 2008-03-05 | 2008-08-06 | 东华大学 | Advanced treatment and reuse of printing wastewater suitable for small and medium-sized printing factories |
CN101700943A (en) * | 2009-11-19 | 2010-05-05 | 东华大学 | A method for advanced treatment and reuse of printing and dyeing wastewater |
CN102180564A (en) * | 2011-03-17 | 2011-09-14 | 东华大学 | Highly-efficient aeration biological filter applied to advanced printing and dyeing wastewater treatment and treatment method thereof |
CN103523996A (en) * | 2013-10-18 | 2014-01-22 | 东华大学 | Treatment device and method of printing and desizing mixed wastewater |
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Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101070216A (en) * | 2007-06-18 | 2007-11-14 | 华南理工大学 | Integrated ozone and aeration biological filtering pool water treatment apparatus and method |
CN101234814A (en) * | 2008-03-05 | 2008-08-06 | 东华大学 | Advanced treatment and reuse of printing wastewater suitable for small and medium-sized printing factories |
CN101700943A (en) * | 2009-11-19 | 2010-05-05 | 东华大学 | A method for advanced treatment and reuse of printing and dyeing wastewater |
CN102180564A (en) * | 2011-03-17 | 2011-09-14 | 东华大学 | Highly-efficient aeration biological filter applied to advanced printing and dyeing wastewater treatment and treatment method thereof |
CN103523996A (en) * | 2013-10-18 | 2014-01-22 | 东华大学 | Treatment device and method of printing and desizing mixed wastewater |
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Address after: 241008 Wuhu economic and Technological Development Zone, North Industrial Park, Anhui Patentee after: Wuhu Fuchun dyeing Limited by Share Ltd Address before: 241008 Wuhu economic and Technological Development Zone, North Industrial Park, Anhui Patentee before: Wuhu Fuchun Dye and Weave Co., Ltd. |