CN204474492U - Polyester waste water treatment system - Google Patents
Polyester waste water treatment system Download PDFInfo
- Publication number
- CN204474492U CN204474492U CN201420816059.3U CN201420816059U CN204474492U CN 204474492 U CN204474492 U CN 204474492U CN 201420816059 U CN201420816059 U CN 201420816059U CN 204474492 U CN204474492 U CN 204474492U
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- Prior art keywords
- waste water
- sludge
- water treatment
- treatment system
- polyester waste
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Abstract
The utility model relates to a kind of Waste Water Treatment, is specifically related to a kind of polyester waste water treatment system.It adopts UASB reaction tank, inner anaerobic sludge concentration is high, Sludge Bed does not establish carrier, save cost and avoid because of filler generation blockage problem, be provided with triphase separator, usually do not establish settling tank, the mud that precipitated district separates comes back in Sludge Bed reaction zone, usually can not establish sludge reflux equipment, run power lower; Comprehensive adjustment pond is mixed sanitary wastewater and polyester waste water, UASB reactor is entered after eddy flow mixing reactor and intermediate pool first are neutralized to PH8-8.5, at utmost can supplement the nutritive elements such as N and P in waste water, ensure that last water purification effluent quality; Be provided with A section activated sludge tank and B level aerobic aeration pond, its waste water treatment efficiency is high, especially in high concentrated organic wastewater process, and stable, construction investment economize and working cost low, have good development prospect.
Description
Technical field
The utility model relates to a kind of Waste Water Treatment, is specifically related to a kind of polyester waste water treatment system.
Background technology
Polyester slice is important experimental branch line raw material, involves the interests of the state and the people.But in the production process of polyester slice, because technique needs certain discharge of wastewater, along with the progressively raising of environmental requirement, the requirement that polyester slice factory effluent is administered is also more and more higher.
Current China polyester production waste water is administered and is still in the starting stage, the features such as it is high that polyester production waste water has Pollutant levels, and the water yield is little, all kinds of nutrition famines, and difficulty of governance is large, difficulty up to standard.The polyester production waste water Processing tecchnics now having dropped into utilization mostly adopts anaerobism+aerobic method, and this processing contaminants clearance is high, and operational path is short, and one-time investment is large, and operation operational management is complicated.
Utility model content
For the deficiency that prior art exists, the utility model provides the polyester waste water treatment system that a kind of detersive efficiency is high, production cost is little and easy and simple to handle.
The utility model is achieved through the following technical solutions:
A kind of polyester waste water treatment system, comprise connect successively polyester waste water equalizing tank, coagulating sedimentation device, comprehensive adjustment pond, eddy flow mixing reactor, intermediate pool first, UASB reaction tank, A section activated sludge tank, settling tank first, B level aerobic aeration pond, settling tank second, intermediate pool second, strainer, active carbon adsorber and discharge pond.
Further, this polyester waste water treatment system also comprises reflux pump first and reflux pump second, and described reflux pump first is arranged between described settling tank first and A section activated sludge tank, and described reflux pump second is arranged between described settling tank second and B level aerobic aeration pond.
Further, this polyester waste water treatment system also comprises recoil pump, and the input terminus of described recoil pump is connected with described discharge pond, and output terminal is connected with described strainer and active carbon adsorber respectively.
Further, this polyester waste water treatment system also comprises sludge thickener, sludge modification device and sludge filter press, described sludge thickener is connected with described reflux pump first, reflux pump second, comprehensive adjustment pond and sludge modification device respectively, and described sludge modification device is arranged between described sludge thickener and sludge filter press.
Compared with prior art, the beneficial effects of the utility model are:
1, employing UASB reaction tank of the present utility model, its inner anaerobic sludge concentration is high, Sludge Bed does not establish carrier, save cost and avoid because of filler generation blockage problem, be provided with triphase separator in UASB, usually do not establish settling tank, the mud that precipitated district separates comes back in Sludge Bed reaction zone, usually can not establish sludge reflux equipment, run power lower;
2, comprehensive adjustment pond of the present utility model is mixed sanitary wastewater and polyester waste water, UASB reactor is entered after eddy flow mixing reactor and intermediate pool first are neutralized to PH8-8.5, at utmost can supplement the nutritive elements such as N and P in waste water, ensure that last water purification effluent quality;
3, be provided with A section activated sludge tank and B level aerobic aeration pond in the utility model, its waste water treatment efficiency is high, especially in high concentrated organic wastewater process, and stable, construction investment economize and working cost low, have good development prospect.
Accompanying drawing explanation
Accompanying drawing is structural representation of the present utility model.
Embodiment
A kind of polyester waste water treatment system, comprise connect successively polyester waste water equalizing tank, coagulating sedimentation device, comprehensive adjustment pond, eddy flow mixing reactor, intermediate pool first, UASB reaction tank, A section activated sludge tank, settling tank first, B level aerobic aeration pond, settling tank second, intermediate pool second, strainer, active carbon adsorber and discharge pond.
Further, this polyester waste water treatment system also comprises reflux pump first and reflux pump second, and described reflux pump first is arranged between described settling tank first and A section activated sludge tank, and described reflux pump second is arranged between described settling tank second and B level aerobic aeration pond.
Further, this polyester waste water treatment system also comprises recoil pump, and the input terminus of described recoil pump is connected with described discharge pond, and output terminal is connected with described strainer and active carbon adsorber respectively.
Further, this polyester waste water treatment system also comprises sludge thickener, sludge modification device and sludge filter press, described sludge thickener is connected with described reflux pump first, reflux pump second, comprehensive adjustment pond and sludge modification device respectively, and described sludge modification device is arranged between described sludge thickener and sludge filter press.
The main body of the upflow type anaerobic bio-reactor (UASB) of this polyester waste water treatment system is divided into upper and lower two regions, namely reaction zone is gentle, liquid, Gu three-phase separation area, good anaerobic mud bed of sedimentation function in the reaction zone of bottom, high concentrated organic wastewater enters reactor bottom by water distribution system, upwards flow through anaerobic mud bed, contact reacts abundant with anaerobic sludge, organism is converted into methane and carbon dioxide, its, liquid, Gu be separated by top three-phase separation area, the clearance of water outlet chemical oxygen demand can reach more than 60%, it is the metabolic characteristic utilizing anerobe that volume bears anaerobic biological treatment, biogas after separation can be used as energy utilization.
Idiographic flow is: polyester waste water enters into polyester waste water equalizing tank, comprehensive adjustment pond is entered after the process of coagulating sedimentation device, add sanitary wastewater simultaneously, eddy flow mixing reactor is entered after the mixing in comprehensive adjustment pond, and add NaOH and NP nutritive medium, after the neutralizing treatment of intermediate pool first, enter UASB reaction tank, then A section activated sludge tank is entered, it runs under anoxic condition, treatment process is made to include some feature of double oxygen process, the pollutent be difficult to by biology directly absorbs in edema with the lung involved can be made effectively to be degraded, there is a large amount of micro-raw floras due to it simultaneously, there is again the returned sluge being several times as much as waste water from reflux pump first, make water quality, the water yield, the load that washes away of pH value and Toxic etc. has huge shock absorption, reflux pump first carries out forced refluence to the mud in settling tank first, reflux ratio is 1:3, waste water effective residence time is 10 hours, ensure effluent quality, enter B level aerobic aeration pond again, its gas-water ratio is 16:1, reflux pump second carries out forced refluence to the mud in settling tank second, reflux ratio is 1:1, effective residence time is 20 hours, it can do pollutent and degrade further, after waste water entered intermediate pool second, strainer and active carbon adsorber process, water purification enters discharge pond, the mud that reflux pump first and reflux pump second produce enters sludge thickener, entered sludge filter press after meeting sludge modification device sedimentation concentration, after dewatering, mud cake was transported outward, used or waste treatment as agriculture fertilizer.
In sum, be only preferred embodiment of the present utility model, not be used for limit the utility model implement scope, all equalizations of doing according to shape, structure, feature and the spirit described in the utility model right change and modify, and all should be included in right of the present utility model.
Claims (4)
1. a polyester waste water treatment system, is characterized in that: comprise connect successively polyester waste water equalizing tank, coagulating sedimentation device, comprehensive adjustment pond, eddy flow mixing reactor, intermediate pool first, UASB reaction tank, A section activated sludge tank, settling tank first, B level aerobic aeration pond, settling tank second, intermediate pool second, strainer, active carbon adsorber and discharge pond.
2. a kind of polyester waste water treatment system according to claim 1, it is characterized in that: described polyester waste water treatment system also comprises reflux pump first and reflux pump second, described reflux pump first is arranged between described settling tank first and A section activated sludge tank, and described reflux pump second is arranged between described settling tank second and B level aerobic aeration pond.
3. a kind of polyester waste water treatment system according to claim 2, it is characterized in that: described polyester waste water treatment system also comprises recoil pump, the input terminus of described recoil pump is connected with described discharge pond, and output terminal is connected with described strainer and active carbon adsorber respectively.
4. a kind of polyester waste water treatment system according to claim 3, it is characterized in that: described polyester waste water treatment system also comprises sludge thickener, sludge modification device and sludge filter press, described sludge thickener is connected with described reflux pump first, reflux pump second, comprehensive adjustment pond and sludge modification device respectively, and described sludge modification device is arranged between described sludge thickener and sludge filter press.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201420816059.3U CN204474492U (en) | 2014-12-19 | 2014-12-19 | Polyester waste water treatment system |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201420816059.3U CN204474492U (en) | 2014-12-19 | 2014-12-19 | Polyester waste water treatment system |
Publications (1)
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CN204474492U true CN204474492U (en) | 2015-07-15 |
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ID=53630295
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
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CN201420816059.3U Expired - Fee Related CN204474492U (en) | 2014-12-19 | 2014-12-19 | Polyester waste water treatment system |
Country Status (1)
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Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN106277587A (en) * | 2016-08-24 | 2017-01-04 | 江苏众胜灭菌设备科技有限公司 | The backwash filter method that a kind of effluent cycle processes |
-
2014
- 2014-12-19 CN CN201420816059.3U patent/CN204474492U/en not_active Expired - Fee Related
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN106277587A (en) * | 2016-08-24 | 2017-01-04 | 江苏众胜灭菌设备科技有限公司 | The backwash filter method that a kind of effluent cycle processes |
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Legal Events
Date | Code | Title | Description |
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C14 | Grant of patent or utility model | ||
GR01 | Patent grant | ||
CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20150715 Termination date: 20211219 |
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CF01 | Termination of patent right due to non-payment of annual fee |