The invention relates to a deep purification and a decentralized treatment and drainage system for tail water of urban sewage treatment plants, and in particular to a tail water decentralized treatment and drainage system of sewage treatment plant that is applied to the technical field of ecological environmental engineering.
At present, the national standard for the discharge of pollutants from urban sewage treatment plants in China is GB18918-2002, with grade A as the highest standard. With the rapid growth of China's economy and the introduction of the concept of ecological civilization construction, the national requirements for the quality of the water environment have become increasingly stringent. In some areas with good water environment quality, if the grade A discharge standard of pollutants in the urban sewage treatment plants is implemented, it will lead to continuous decline in water environment quality, which is apparently unable to meet the requirements for the water environment functional zoning. If an urban sewage treatment plant is expanded or reconstructed, or upgraded, it will usually need high investment but the effect may be not obvious, which does not comply with the requirement of ecological water control. In the urban sewage treatment plants, usually the treated sewage is collected to a main drainage pipe and then discharged into a river nearby. Therefore, the point source pollution of the water outlets of urban sewage treatment plants is more serious. For sewage treatment plants whose sewage is discharged from a concentrated place, when the effluent water quality of the wastewater treatment plant is unstable, there are drawbacks of sudden deterioration of water quality at the sewage outlet and its downstream, low transparency and more foams, etc., affecting the sensory effect of water body and water quality assessment.
The technical problem to be solved by the present invention is to provide a decentralized treatment and drainage system with low operating cost and low energy consumption that is capable of improving the tail water quality of sewage treatment plants. To achieve this object, the present invention adopts the following technical solutions:
A tail water decentralized treatment and drainage system of sewage treatment plant, comprising a riparian vegetation buffer zone, a subsurface flow constructed wetland and a riverside protection pile; the riparian vegetation buffer zone comprises an excavation protection slope, and an ecological bag is paved on the surface of the excavation protection slope, an intercepting ditch is provided between the riparian vegetation buffer zone and the subsurface flow constructed wetland; the subsurface flow constructed wetland has a water inlet system and a water drainage system;
The subsurface flow constructed wetland is disposed on the river protection slope along the river flow direction, the subsurface flow constructed wetland is provided with a treatment system, a water drainage system and a plurality of outlet pipes disposed along the river flow direction;
Tail water discharged from a sewage treatment plant enters a treatment system of the subsurface flow constructed wetland through the water inlet system, and the outlet water at the bottom of the subsurface flow constructed wetland enters the water drainage system to discharge to a river through the plurality of outlet pipes.
While adopting the foregoing technical solutions, the present invention further adopts or combines the following technical solutions:
The slope of the excavation protection slope is between 1:1.5 and 1:3, and forms a stepped soil slope structure, and the ecological bag is placed on the soil slope structure layer by layer.
The ecological bag contains an outer packaging bag, the bag is provided with mixed packing.
The outer packaging bag is made of a geotextile material that is non-woven fabric and needled into a net; the mixed packing contains cultivated soil and grass seeds, suitable for plant growth; a three-dimensional coupling buckle is used to connect ecological bags, an ecological bag and an excavation protection slope; the adjacent ecological bags are mutually connected and the ecological bag is connected with the excavation protection slope by the three-dimensional coupling buckle using spur structures on the upper and lower surfaces thereof, to form a stable triangular internal friction and contraction structure.
The water inlet system comprises a water inlet manifold, a valve well, a valve and a diverting pipe; the treatment system comprises a wetland structure, a filter bed purification unit, a wetland plant, and the wetland plant is planted above the filter bed purification unit, the water drainage system comprises a water outlet regulating pond, an outlet pipe, and an air duct;
The diverting pipe is introduced to the upper part of the filter bed purging unit; the air duct is introduced to the bottom of the filter bed purification unit, and communicated through a communicating pipe at the bottom, and the communicating pipe is provided with a vent hole.
The treatment system of the subsurface flow constructed wetland is provided by units, a plurality of treatment units are provided along the river flow direction, the water drainage system forms a channel type water outlet regulating pond along a river flow direction, and the plurality of outlet pipes are connected to the water outlet regulating pond.
The three-dimensional coupling buckle comprises a connecting motherboard, an upper burr and a lower burr, the upper burr is in the middle of the upper surface of the connecting motherboard, the lower burr is in the lower surface of the connecting motherboard, and the lower burr is beyond both sides of the upper burr, to form a triangle-arranged structure adapted to the triangular internal friction and contraction structure.
The wetland structure comprises an outer wall, a partition wall, a ground beam and a ring beam; the filter bed purification unit comprises a cushion layer, an impermeable membrane, a geotextile and a multi-graded filter layer from bottom to top;
The wetland structure forms a plurality of unit spaces arranged in the direction of the water flow of the river, and each unit space is provided with the filter bed purification unit.
The outer wall and the partition wall are brick-concrete structures, the ground beam and the ring beam are reinforced concrete structures; the cushion layer comprises a gravel cushion layer, a concrete cushion layer, and a sand cushion layer from the bottom to the top; the impermeable membrane is a high-density polyethylene membrane having a thickness of 1.2 mm; the geotextile has a thickness of 2 mm; the multi-graded filter layer comprises a gravel filter layer with a particle size of 16˜32 mm, a gravel filter layer with a particle size of 8˜16 mm, a zeolite filter layer with a particle size of 5˜8 mm, and a gravel filter layer with a particle size of 8˜16 mm from bottom to top.
The riverside protection pile is a concrete structure, piling into the waterfront of water outlet of the subsurface flow constructed wetland, and arranged linearly along the river bank.
The present invention is novel in idea and reasonable in design. By constructing a subsurface flow constructed wetland on the slope of the river bank after repositioning, the vegetation buffer zone and the subsurface flow constructed wetland are skillfully combined to achieve the conversion from point source centralized discharge to linear decentralized discharge of tail water of sewage treatment plants. The tail water of sewage treatment plants is purified and treated through the subsurface flow constructed wetland, to give full play to the self-purification capability of river water, reduce the pressure of local sewage discharge point of the river and avoid rapid deterioration of water quality. In addition, river environment is rebuilt while managing tail water pollution, to achieve a comprehensive effect at a cost. It is particularly suitable for changing the condition of single drainage outlet for the sewage treatment plant constructed near the river, with strong practicability.
Notes: riparian vegetation buffer zone 1, subsurface flow constructed wetland 2, riverside protection pile 3, excavation protection slope 4, ecological bag 5, intercepting ditch 6, water inlet system 7, treatment system 8, water drainage system 9, outer packaging bag 10, mixed packing in the bag 11, three-dimensional coupling buckle 12, water inlet manifold 13, valve well 14, diverting pipe 16, wetland structure 17, filter bed purification unit 18, wetland plant 19, water outlet regulating pond 20, outlet pipe 21, air duct 22, communicating pipe 23, outer wall 27, partition wall 28, ground beam 29, ring beam 30, cushion layer 31, impermeable membrane 32, geotextile 33, multi-graded filter layer 34, gravel cushion layer 35, concrete cushion layer 36, sand cushion layer 37, gravel filter layer with particle size of 16˜32 mm 38, gravel filter layer with particle size of 8˜16 mm 39, zeolite filter layer with particle size of 5˜8 mm 40, gravel filter layer with particle size of 8˜16 mm 41.
The present invention is described in detail in combination with attached drawings and embodiments.
The present invention provides a tail water decentralized treatment and drainage system of sewage treatment plant, comprising a riparian vegetation buffer zone 1, a subsurface flow constructed wetland 2 and a riverside protection pile 3.
Wherein, the riparian vegetation buffer zone 1 comprises an excavation protection slope 4 and an ecological bag 5 stacked on the excavation protection slope. The runoff inflow pollution caused by rainfall can be effectively reduced by the plant absorption effect of ecological bag 5, to avoid the impact of pollutants in the primary rain on subsurface flow constructed wetland 2. The subsurface flow constructed wetland 2 is arranged on the river protection slope, and the subsurface flow constructed wetland has a water inlet system 7 and a water drainage system 9. The water inlet system 7 introduces the tail water of the sewage treatment plant into the subsurface flow constructed wetland 2 through the water inlet manifold 13, the valve well 14, the valve 15 and the diverting pipe 16, and further purifies the tail water by the physical, chemical and biological effects of the treatment system 8 in the subsurface flow constructed wetland 2, finally the effluent is discharged into the adjacent rivers by the multiple drainage pipes of the water drainage system arranged along the river bank, to achieve the purpose of reduced discharge and decentralized discharge of pollutants in the tail water.
As shown in
The multi-graded filter layer 34 in the subsurface flow construct wetland 2 has the purification effects of adsorption and sedimentation. The wetland plant 19 planted on the surface has effect on absorption and utilization of pollutants. After the tail water passes through the subsurface flow constructed wetland, the nitrogen and phosphorous pollutants and suspended particulate matters have been greatly reduced, finally the wetland effluent is uniformly dispersed and discharged into rivers from various treatment units through the water drainage system 9, changing the original point source discharge from sewage treatment plants.
The water drainage system 9 comprises a water outlet regulating pond 20, an outlet pipe 21, an air duct 22 and a communicating pipe 23. The water outlet regulating pond 20 can stably regulate the amount of water discharged from the subsurface flow constructed wetland based on the siphoning phenomenon of the U-shaped pipe. The effluent from the bottom of the subsurface flow constructed wetland 2 flows into the water outlet regulating pond 20, and then discharge the purified water into rivers through outlet pipe 21 from the water outlet regulating pond 20. The air duct 22 is connected to the bottom of the filter bed purification unit 18, and communicated with the communicating pipe at the bottom, and a vent hole is set in the communicating pipe. The water outlet regulating pond 20 preferably forms a channel type water outlet regulating pond 20 along the river flow direction, and a plurality of outlet pipes 21 are arranged along the river flow direction to achieve drainage in a uniform and distributed manner.
The water inlet manifold 13 is a polyethylene pipe, the valve well 14 is a steel-concrete structure, the valve 15 is an electric valve, the diverting pipe 16 is a spiral welded pipe, and the outlet pipe 21 and the air duct 22 are hard PVC pipes.
The wetland structure 17 comprises an outer wall 27, a partition wall 28, a ground beam 29, and a ring beam 30 (please supplement the positional relationship of the structures in the treatment system). The wetland structure 17 forms a plurality of unit spaces arranged along the direction of the river flow. Each unit space is provided with the filter bed purification unit 18. The filter bed purification unit 18 comprises a cushion layer 31, an impermeable membrane 32, a geotextile 33, and a multi-graded filter layer 34 sequentially from the bottom to the top. The communication portion of the air duct 22 is between the multi-graded filter layer 34 and the cushion layer 31. The wetland plant 19 may include Cyperus alternifolius, Thalia dealbata, cattails, scallions, reeds, and so on.
The outer wall 27 and the partition wall 28 are brick-concrete structures, the ground beam 29 and the ring beam 30 are reinforced concrete structures; the cushion layer 31 comprises a gravel cushion layer 35, a concrete cushion layer 36 and a sand cushion layer 37 from bottom to top; the impermeable membrane 32 is a high-density polyethylene membrane having a thickness of 1.2 mm; the geotextile 33 has a thickness of 2 mm; and the multi-graded filter layer 34 comprises a gravel filter layer 38 with a particle size of 16˜32 mm, a gravel filter layer 39 with a particle size of 8˜16 mm, a zeolite filter layer 40 with a particle size of 5˜8 mm, and a gravel filter layer 41 with a particle size of 8˜16 mm from bottom to top. The multiple grades of the filter material can increase the stability between layers. The multi-graded filter layer 34 is the core part of the wastewater treatment system 8, of which, the zeolite filter layer 40 with a particle size of 5˜8 mm has the strongest pollutant removal capability.
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The mixed packing in the bag adopts clean granular mixture suitable for plant growth, about 30% of the packing is gravel, and about 70% is cultivated soil. 10 to 15 g of grass seeds are mixed per square meter, when germinating in the ecological bag, grass seeds will come out of the surface of the outer packaging bag and grow rapidly, to form dense green vegetation. When splicing the ecological bag horizontally, the edges of the ecological bag should be tightly aligned, and then the outer packaging bag of the ecological bag should be pierced with the spur structure of the three-dimensional coupling buckle, to prevent affecting the structural stability of ecological bags due to dislocation.
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The foregoing descriptions are merely specific embodiments of the present invention, but the structural features of the present invention are not limited thereto. Any changes or modifications made by those skilled in the art within the scope of the present invention shall fall within the scope of protection of the present invention.
Number | Date | Country | Kind |
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201721008278.9 | Aug 2017 | CN | national |