Alcohol wastewater treatment system
Technical Field
The utility model relates to a sewage treatment field, especially an alcohol effluent disposal system.
Background
With the rapid development of industry, the variety and quantity of waste water are rapidly increased, the pollution to water is becoming wide and serious, and the health and safety of human beings are threatened. Since the composition of industrial waste water is more complex and some are toxic, it is also more important that industrial waste water treatment is more difficult than municipal waste water treatment. The alcohol wastewater is organic wastewater with high concentration, high temperature and high suspended matter, and the treatment technology starts earlier and develops faster.
The waste residue in the waste liquid contains crude fibers such as crushed cassava skin, rhizomes and the like, and the substances are insoluble COD in the waste water; cellulose and hemicellulose in cassava are polysaccharide substances, cannot be used as a carbon source of yeast in alcohol fermentation, and remain in waste liquid to be expressed as soluble COD; silt impurities of inorganic ash. These substances increase the difficulty of wastewater treatment.
The prior patent technologies mainly focus on the process of flocculation adsorption and precipitation, for example, patent numbers CN201210483774 and CN201510220252 are all based on flocculation adsorption of CODcr, so as to improve the removal efficiency of CODcr. However, the removal effect of these treatments is not very significant, resulting in a high subsequent biochemical load. Therefore, the market at present needs a wastewater treatment agent which not only can realize flocculation, but also can efficiently remove CODcr.
Disclosure of Invention
An object of the utility model is to provide an alcohol wastewater treatment system to satisfy the alcohol wastewater to high concentration, high temperature, high suspended solid and handle, make it reach emission standard.
For realizing above-mentioned technical purpose, reach above-mentioned technological effect, the utility model discloses an alcohol effluent disposal system, the aeration sand setting section that has loop through sewage pipe connection setting has been included, acidizing anaerobic section, the secondary sedimentation section, anaerobic degradation section and water collection discharge section, aeration sand setting section has included aeration sand setting catch basin, acidizing anaerobic section has included acidizing equalizing basin and full mixed formula anaerobic reactor, the secondary sedimentation section has included the sedimentation tank, the catch basin, coagulating gas floating machine and middle pond, anaerobic degradation section has included UASB reactor and SBR reactor, the water collection discharge section has included the discharge pond, aeration sand setting catch basin, the acidizing equalizing basin, full mixed formula anaerobic reactor, the catch basin, middle pond and discharge pond bottom all are provided with the sewage elevator pump, the sewage elevator pump is connected the sewage pipe cooperation and is carried.
Wherein, aeration sand setting catch basin has included aeration sand setting pond and just sinks the catch basin, and aeration sand setting pond inside is provided with aeration line and fortune sand subassembly, and fortune sand subassembly sets up in aeration line below, just sinks the catch basin bottom and is provided with the sewage elevator pump.
Wherein, the bottom of the full-mixing anaerobic reactor is provided with a water distributor which is communicated with a lift pump in the primary sedimentation water collecting tank through a sewage pipeline.
Preferably, the system also comprises a plurality of groups of methane pipeline components and a water seal device, wherein the methane pipeline components are communicated in parallel and are respectively connected with the totally-mixed anaerobic reactor and the UASB reactor, and the water seal device is arranged at the tail end of the methane pipeline components.
Preferably, the device also comprises a horizontal screw separator which is arranged between the sedimentation tank and the water collecting tank and is communicated with the sedimentation tank and the water collecting tank through a sewage pipeline.
Preferably, the system also comprises a spiral plate type heat exchanger, wherein the spiral plate type heat exchanger is arranged outside the acidification adjusting tank and is communicated with the acidification adjusting tank through a sewage pipeline.
Preferably, the system also comprises a siphon decanter which is arranged inside the SBR reactor and is connected with a discharge water tank through a sewage pipeline.
Preferably, the system also comprises a Rotz blower which is respectively connected with the SBR reactor and an aeration pipeline in the aeration grit collecting tank through air pipelines.
Preferably, the system also comprises a sludge concentration tank, a sludge reactor and a belt filter press, wherein the sludge concentration tank is communicated with the bottom of the SBR reactor, the bottom of the fully-mixed anaerobic reactor, the bottom of the coagulation air flotation machine and the bottom of the UASB reactor through sludge pipelines, one end of the sludge reactor is connected with the sludge concentration tank through a sludge pipeline, and the other end of the sludge reactor is connected with the belt filter press.
The utility model discloses following beneficial effect has:
1. the utility model discloses a configuration optimization design, through carrying out mud, the sewage separation many times to the alcohol waste water of high suspended solid, improve the accurate nature of separation to mud occupies the space of reactor in reducing each reactor, improves the treatment effect of sewage.
2. The reasonably treated alcohol wastewater treatment system improves the treatment of alcohol wastewater through multiple reaction adjustment and physical separation, and improves the reutilization of alcohol wastewater by properly recycling methane, sewage and sludge generated in the treatment process.
Drawings
Fig. 1 is a schematic structural diagram of the present invention.
Description of the main part symbols:
1: aeration grit chamber, 2: primary sedimentation water collecting tank, 3: aeration pipeline, 4: sand conveying assembly, 5: sewage lift pump, 6: acidification adjusting tank, 7: fully-mixed anaerobic reactor, 8: water distributor, 9: biogas pipeline assembly, 10: spiral plate heat exchanger, 11: sedimentation tank, 12: catch basin, 13: coagulation air flotation machine, 14: intermediate pool, 15: horizontal screw separator, 16: UASB reactor, 17: SBR reactor, 18: siphon decanter, 19: drain tank, 20: water seal, 21: roots blower, 22: sludge thickener, 23: sludge reactor, 24: belt filter press, 25: sewer line, 26: air duct, 27: a sludge pipeline.
Detailed Description
In order to make the objects, technical solutions and advantages of the present invention more clearly understood, the present invention is further described in detail below with reference to the accompanying drawings and embodiments.
As shown in fig. 1, the utility model discloses an alcohol wastewater treatment system, which comprises an aeration sand setting section, an acidification anaerobic section, a secondary settling section, an anaerobic degradation section and a water collecting and discharging section which are sequentially connected and arranged through a sewage pipeline 25, wherein the aeration sand setting section comprises an aeration sand setting water collecting tank, the aeration sand setting water collecting tank comprises an aeration sand setting tank 1 and a primary settling water collecting tank 2, an aeration pipeline 3 and a sand conveying component 4 are arranged in the aeration sand setting tank 1, the sand conveying component 4 is arranged below the aeration pipeline 3, and a sewage lifting pump 5 is arranged at the bottom of the primary settling water collecting tank 2; the acidification anaerobic section comprises an acidification adjusting tank 6 and a fully mixed anaerobic reactor 7, the bottom of the fully mixed anaerobic reactor 7 is provided with a water distributor 8, the water distributor 8 is communicated with a sewage lifting pump 5 in the primary sedimentation water collecting tank 2 through a sewage pipeline 25, and the fully mixed anaerobic reactor 7 is also connected with a methane pipeline component 9; the system also comprises a spiral plate type heat exchanger 10, wherein the spiral plate type heat exchanger 10 is arranged outside the acidification adjusting tank 6 and is communicated with the acidification adjusting tank through a sewage pipeline 25; the secondary sedimentation section comprises a sedimentation tank 11, a water collecting tank 12, a coagulation air floatation machine 13, an intermediate water tank 14 and a horizontal screw separator 15, wherein the horizontal screw separator 15 is arranged between the sedimentation tank 11 and the water collecting tank 12 and is communicated with each other through a sewage pipeline 25; the anaerobic degradation section comprises a UASB reactor 16, an SBR reactor 17 and a siphon decanter 18, wherein the siphon decanter 18 is arranged inside the SBR reactor 17 and is connected with a discharge water tank 19 through a sewage pipeline 25; the UASB reactor 16 is connected with biogas pipeline components 9, a plurality of groups of biogas pipeline 9 components are communicated in parallel and are respectively connected with the full-mixing type anaerobic reactor 7 and the UASB reactor 16, and the water seal device 20 is arranged at the tail end of the biogas pipeline components 9; the catchment discharge section comprises a discharge basin 19; the bottom of the aeration grit water collecting tank, the acidification adjusting tank 6, the full-mixing type anaerobic reactor 7, the water collecting tank 12, the intermediate water tank 14 and the discharge water tank 19 are all provided with a sewage lifting pump 5, the sewage lifting pump 5 is connected with a sewage pipeline 25 for matched conveying, the device also comprises a Rotz blower 21, and the Rotz blower 21 is respectively connected with the SBR reactor 17 and an aeration pipeline 3 in the aeration grit water collecting tank through an air pipeline 26.
The system also comprises a sludge concentration tank 22, a sludge reactor 23 and a belt filter press 24, wherein the sludge concentration tank 22 is communicated with the bottom of the SBR reactor 17, the bottom of the full-mixing type anaerobic reactor 7, the bottom of the coagulation air floatation machine 13 and the bottom of the UASB reactor 16 through a sludge pipeline 27, one end of the sludge reactor 23 is connected with the sludge concentration tank 22 through the sludge pipeline 27, and the other end is connected with the belt filter press 24.
The working principle is as follows:
in the utility model, alcohol wastewater is connected with an aeration grit chamber 1 through a sewage pipeline 25 to carry out preliminary sediment deposition and outward transportation and removal, the deposited sediment of a fully mixed anaerobic reactor 7, a coagulation air flotation machine 13, a UASB reactor 16 and a SBR reactor 17 in subsequent working sections is collected, gathered into a sludge concentration tank 22 and pressed into a mud cake and then outward transported and discharged, the deposited sediment of a sedimentation tank 11 is separated, discharged and outward transported through a horizontal spiral separator 15, marsh gas generated in the reaction process of the UASB reactor 16 is separated and recycled through a water seal 20, sewage in a treatment system is subjected to multiple reaction treatments, the sewage enters a discharge tank 19 and then can be supplied to a spiral plate type heat exchanger 10 to be used as cooling water for heat exchange, and then enters an acidification regulation tank 6 to be used for acidification regulation, the recycling can meet the requirements of treating alcohol wastewater with high concentration, high temperature and high suspended matters, so that the emission standard is reached.
The above description is only for the preferred embodiment of the present invention, but the scope of the present invention is not limited thereto, and any changes or substitutions that can be easily conceived by those skilled in the art within the technical scope of the present invention should be covered by the present invention.