SUMMERY OF THE UTILITY MODEL
An object of the utility model is to provide a high-efficient compound stream constructed wetland system, the utility model discloses regularly with the deposit that the wetland operation in-process produced, hold back the thing and the biomembrane discharge wetland unit that peels off, rivers are unblocked in the assurance wetland.
In order to solve the technical problem, the utility model discloses a following technical scheme: a high-efficiency composite flow constructed wetland system comprises a grid regulating tank, a full-automatic backwashing filter, a high-efficiency composite flow constructed wetland, a pipeline A and a pipeline B, wherein the grid regulating tank is connected with the full-automatic backwashing filter through the pipeline A, and the full-automatic backwashing filter is connected with the high-efficiency composite flow constructed wetland through the pipeline B; and (3) regularly discharging sediments, trapped matters and peeled biological membranes generated in the wetland operation process out of the wetland unit to ensure smooth water flow in the wetland.
The grid regulating tank comprises a grid well and a hydrolysis acidification regulating tank, the grid well is connected with the hydrolysis acidification regulating tank, an elastic three-dimensional filler and a water inlet pump are arranged in the hydrolysis acidification regulating tank, the water inlet pump is connected with a pipeline A, and a valve A is arranged on the pipeline A; the elastic three-dimensional filler intercepts and adsorbs small particles, decomposes macromolecular organic matters into small molecules convenient for oxidation treatment, removes partial organic matters, improves the biodegradability of wetland water inflow, and the effluent has no bad smell of anaerobic fermentation, so that the surrounding environment is not influenced.
The high-efficiency composite flow constructed wetland system comprises a vertical flow constructed wetland, a horizontal subsurface flow constructed wetland, a water outlet well and a membrane inversion well, wherein a water inlet channel is arranged between the vertical flow constructed wetland and the horizontal subsurface flow constructed wetland and is arranged on the side wall of the bottom of the vertical flow constructed wetland; the sewage is divided into two parts, one part directly enters the vertical flow artificial wetland, the other part directly enters the bottom of the horizontal subsurface flow artificial wetland to carry out denitrification reaction with the nitrifying liquid, the denitrification is carried out, the water inlet channel enables the sewage between the vertical flow artificial wetland and the horizontal subsurface flow artificial wetland to be mixed, and the backwashing pipeline carries out backwashing treatment on the high-efficiency composite flow artificial wetland.
In the efficient composite flow artificial wetland system, the upper part of the vertical flow artificial wetland is provided with a water distribution perforated pipe a, a plurality of water distribution holes a are equidistantly distributed on the water distribution perforated pipe a, the aperture of the water distribution holes a is 10mm, the lower part of the vertical flow artificial wetland is provided with a film falling perforated pipe a, a plurality of film falling holes a are equidistantly distributed on the film falling perforated pipe a, and the aperture of the film falling holes a is 20 mm; the A water distribution perforated pipe is used for carrying out water distribution treatment on the vertical flow artificial wetland, and the A inverted film perforated pipe is used for carrying out dredging treatment on the vertical flow artificial wetland.
The high-efficiency composite flow constructed wetland system is characterized in that an A partition plate and a B partition plate are arranged in the horizontal subsurface flow constructed wetland, the left side of the A partition plate is connected with the inner wall of the horizontal subsurface flow constructed wetland, the distance between the right side of the A partition plate and the inner wall of the horizontal subsurface flow constructed wetland is D1, the right side of the B partition plate is connected with the inner wall of the horizontal subsurface flow constructed wetland, the distance between the left side of the B partition plate and the inner wall of the horizontal subsurface flow constructed wetland is D2, D1 is D2, the A partition plate is arranged below the B partition plate, a water inlet channel is arranged below the A partition plate, a water collecting perforated pipe is arranged above the B partition plate, the water collecting perforated pipe is connected with a water outlet well, a plurality of water collecting holes are distributed on the water collecting perforated pipe at equal intervals, the aperture of the water collecting holes is 15mm, a B water distribution perforated pipe and a B inverted film perforated pipe are arranged at the lower part of the horizontal subsurface flow constructed wetland, and the B water distribution perforated pipe and the B inverted film perforated pipe are both arranged below the B partition plate, a plurality of water distribution holes B are distributed on the water distribution perforated pipe B at equal intervals, the aperture of the water distribution holes B is 10mm, a plurality of inverted film holes B are distributed on the inverted film perforated pipe B at equal intervals, and the aperture of the inverted film holes B is 20 mm; a partition plate A and a partition plate B are arranged in the horizontal subsurface flow constructed wetland and are designed into a horizontal baffle plate flow form, the vertical flow constructed wetland forms flooding and drying conditions of the wetland by periodically feeding and discharging water to realize natural oxygenation, fully nitrifies organic matters and then enters the horizontal subsurface flow constructed wetland, an aerobic and anaerobic environment is formed by designing a horizontal flow folded plate, the nitrification and denitrification effects are enhanced, the overall nitrogen and phosphorus removal effect of the system is improved, a water distribution perforated pipe B performs water distribution treatment on the horizontal subsurface flow constructed wetland, and a membrane inversion perforated pipe B performs desilting treatment on the horizontal subsurface flow constructed wetland.
In the high-efficiency composite flow constructed wetland system, a vertical flow wetland planting layer is arranged in the vertical flow constructed wetland, a horizontal subsurface flow wetland planting layer is arranged in the horizontal subsurface flow constructed wetland, the vertical flow wetland planting layer is sequentially provided with a coarse sand layer with the thickness of 100mm, a gravel layer with the thickness of 500mm, a zeolite layer with the thickness of 500mm, a coarse sand layer with the thickness of 200mm and planting soil with the thickness of 200mm from bottom to top, the horizontal subsurface flow wetland planting layer is sequentially provided with a coarse sand layer with the thickness of 100mm, a blast furnace slag layer with the thickness of 400mm, a dolomite layer with the thickness of 400mm, a coarse sand layer 36 with the thickness of 200mm and planting soil with the thickness of 200mm from bottom to top, a plurality of plants are arranged on the planting soil at equal intervals, the particle size of coarse sand in the coarse sand layer is 0.9-1.2mm, the particle size in the gravel layer is 80-120mm, and the particle size of zeolite in the zeolite layer is 20-60mm, the grain size of the blast furnace slag in the blast furnace slag layer is 80-120mm, and the grain size of the dolomite in the dolomite layer is 15-60 mm.
According to the efficient composite flow constructed wetland system, the water distribution perforated pipe A is connected with the water inlet branch pipe A, the film pouring perforated pipe A is connected with the film pouring well through a pipeline, and an E valve is arranged on a pipe section between the film pouring perforated pipe A and the film pouring well.
According to the efficient composite flow constructed wetland system, the water distribution perforated pipe B is connected with the water inlet branch pipe B, the film pouring perforated pipe B is connected with the film pouring well pipeline, and an F valve is arranged on a pipe section between the film pouring perforated pipe B and the film pouring well.
In the high-efficiency composite flow constructed wetland system, a G valve is arranged on a pipe section between the water collecting perforated pipe and the water outlet well, a C pipe and a D pipe are arranged on a pipe section between the G valve and the water collecting perforated pipe, an H valve is arranged on the C pipe, an I valve is arranged on the D pipe, one end of the D pipe is connected to the pipe section between the G valve and the water collecting perforated pipe, and the other end of the D pipe is connected to the pipe section between the D valve and the lift pump; the G valve and the H valve are adjusted to open according to different high and low liquid levels of the water outlet well, the H valve is opened when the inflow water is large, and the G valve is opened when the inflow water is small.
Compared with the prior art, the utility model comprises a grid adjusting tank, a full-automatic back-flushing filter, a high-efficiency composite flow constructed wetland, a pipeline A and a pipeline B, wherein the grid adjusting tank is connected with the full-automatic back-flushing filter through the pipeline A, the full-automatic back-flushing filter is connected with the high-efficiency composite flow constructed wetland through the pipeline B, the grid adjusting tank comprises a grid well and a hydrolysis acidification adjusting tank, the grid well is connected with the hydrolysis acidification adjusting tank, an elastic three-dimensional filler and a water inlet pump are arranged in the hydrolysis acidification adjusting tank, the water inlet pump is connected with the pipeline A, the pipeline A is provided with a valve, the high-efficiency composite flow constructed wetland comprises a vertical flow constructed wetland, a horizontal subsurface flow constructed wetland, a water outlet well and a membrane inversion well, the pipeline B comprises a water inlet branch pipe A and a water inlet branch pipe B, the water inlet branch pipe A is provided with a valve B, the water inlet branch pipe B is provided with a valve C, the utility model also provides an implementation method of high-efficient compound flow constructed wetland system, the utility model discloses regularly with the deposit that the wetland operation in-process produced, the biomembrane discharge wetland unit that holds back the thing and peel off, guarantee that rivers are unblocked in the wetland, the three-dimensional filler of elasticity intercepts the little particulate matter of absorption, decompose into the micromolecule of oxidation treatment of being convenient for with the macromolecule organic matter, and get rid of partial organic matter, improve the biodegradability that the wetland was intake, go out the bad smell that does not have anaerobic fermentation, can not influence the environment on every side, divide into two parts with sewage, partly directly gets into vertical flow constructed wetland, the bottom that another part directly gets into horizontal undercurrent constructed wetland carries out denitrification with the nitrifying liquid, carry out the denitrogenation.
Detailed Description
Embodiment 1 of the utility model: a high-efficiency composite flow constructed wetland system comprises a grid regulating tank 1, a full-automatic backwashing filter 2, a high-efficiency composite flow constructed wetland 3, an A pipeline 4 and a B pipeline 5, wherein the grid regulating tank 1 is connected with the full-automatic backwashing filter 2 through the A pipeline 4, and the full-automatic backwashing filter 2 is connected with the high-efficiency composite flow constructed wetland 3 through the B pipeline 5; and (3) regularly discharging sediments, trapped matters and peeled biological membranes generated in the wetland operation process out of the wetland unit to ensure smooth water flow in the wetland.
Embodiment 2 of the utility model: a high-efficiency composite flow constructed wetland system comprises a grid regulating tank 1, a full-automatic backwashing filter 2, a high-efficiency composite flow constructed wetland 3, an A pipeline 4 and a B pipeline 5, wherein the grid regulating tank 1 is connected with the full-automatic backwashing filter 2 through the A pipeline 4, and the full-automatic backwashing filter 2 is connected with the high-efficiency composite flow constructed wetland 3 through the B pipeline 5; the sediments, the trapped matters and the peeled biological membranes generated in the wetland operation process are discharged out of the wetland unit at regular intervals, so that the water flow in the wetland is ensured to be smooth; the grid adjusting tank 1 comprises a grid well 6 and a hydrolysis acidification adjusting tank 7, the grid well 6 is connected with the hydrolysis acidification adjusting tank 7, an elastic three-dimensional filler 8 and a water inlet pump 9 are arranged in the hydrolysis acidification adjusting tank 7, the water inlet pump 9 is connected with the pipeline A4, and the pipeline A4 is provided with a valve A10; the elastic three-dimensional filler 8 intercepts and adsorbs small particles, decomposes macromolecular organic matters into small molecules convenient for oxidation treatment, removes partial organic matters, improves the biodegradability of wetland water inflow, and has no bad smell of anaerobic fermentation when yielding water, thereby not affecting the surrounding environment.
Embodiment 3 of the utility model: a high-efficiency composite flow constructed wetland system comprises a grid regulating tank 1, a full-automatic backwashing filter 2, a high-efficiency composite flow constructed wetland 3, an A pipeline 4 and a B pipeline 5, wherein the grid regulating tank 1 is connected with the full-automatic backwashing filter 2 through the A pipeline 4, and the full-automatic backwashing filter 2 is connected with the high-efficiency composite flow constructed wetland 3 through the B pipeline 5; the sediments, the trapped matters and the peeled biological membranes generated in the wetland operation process are discharged out of the wetland unit at regular intervals, so that the water flow in the wetland is ensured to be smooth; the grid adjusting tank 1 comprises a grid well 6 and a hydrolysis acidification adjusting tank 7, the grid well 6 is connected with the hydrolysis acidification adjusting tank 7, an elastic three-dimensional filler 8 and a water inlet pump 9 are arranged in the hydrolysis acidification adjusting tank 7, the water inlet pump 9 is connected with the pipeline A4, and the pipeline A4 is provided with a valve A10; the elastic three-dimensional filler 8 intercepts and adsorbs small particles, decomposes macromolecular organic matters into small molecules convenient for oxidation treatment, removes partial organic matters, improves the biodegradability of wetland inlet water, and ensures that the outlet water has no bad smell of anaerobic fermentation and does not influence the surrounding environment; the high-efficiency composite flow artificial wetland 3 comprises a vertical flow artificial wetland 11, a horizontal subsurface flow artificial wetland 12, a water outlet well 13 and a membrane pouring well 14, wherein a water inlet channel 50 is arranged between the vertical flow artificial wetland 11 and the horizontal subsurface flow artificial wetland 12, the water inlet channel 50 is arranged on the side wall of the bottom of the vertical flow artificial wetland 11, the B pipeline 5 comprises an A water inlet branch pipe 15, a B water inlet branch pipe 16 and a backwashing pipeline 17, the A water inlet branch pipe 15 is provided with a B valve 18, the B water inlet branch pipe 16 is provided with a C valve 19, the backwashing pipeline 17 is provided with a D valve 20, the bottom of the water outlet well 13 is provided with a lifting pump 21, and the backwashing pipeline 17 is connected with the lifting pump 21; the sewage is divided into two parts, one part directly enters the vertical flow artificial wetland, the other part directly enters the bottom of the horizontal subsurface flow artificial wetland to carry out denitrification reaction with the nitrifying liquid, the water inlet channel 50 mixes the sewage between the vertical flow artificial wetland 11 and the horizontal subsurface flow artificial wetland 12, and the back flushing pipeline 17 carries out back flushing treatment on the high-efficiency composite flow artificial wetland 3.
Embodiment 4 of the utility model: a high-efficiency composite flow constructed wetland system comprises a grid regulating tank 1, a full-automatic backwashing filter 2, a high-efficiency composite flow constructed wetland 3, an A pipeline 4 and a B pipeline 5, wherein the grid regulating tank 1 is connected with the full-automatic backwashing filter 2 through the A pipeline 4, and the full-automatic backwashing filter 2 is connected with the high-efficiency composite flow constructed wetland 3 through the B pipeline 5; the sediments, the trapped matters and the peeled biological membranes generated in the wetland operation process are discharged out of the wetland unit at regular intervals, so that the water flow in the wetland is ensured to be smooth; the grid adjusting tank 1 comprises a grid well 6 and a hydrolysis acidification adjusting tank 7, the grid well 6 is connected with the hydrolysis acidification adjusting tank 7, an elastic three-dimensional filler 8 and a water inlet pump 9 are arranged in the hydrolysis acidification adjusting tank 7, the water inlet pump 9 is connected with the pipeline A4, and the pipeline A4 is provided with a valve A10; the elastic three-dimensional filler 8 intercepts and adsorbs small particles, decomposes macromolecular organic matters into small molecules convenient for oxidation treatment, removes partial organic matters, improves the biodegradability of wetland inlet water, and ensures that the outlet water has no bad smell of anaerobic fermentation and does not influence the surrounding environment; the high-efficiency composite flow artificial wetland 3 comprises a vertical flow artificial wetland 11, a horizontal subsurface flow artificial wetland 12, a water outlet well 13 and a membrane pouring well 14, wherein a water inlet channel 50 is arranged between the vertical flow artificial wetland 11 and the horizontal subsurface flow artificial wetland 12, the water inlet channel 50 is arranged on the side wall of the bottom of the vertical flow artificial wetland 11, the B pipeline 5 comprises an A water inlet branch pipe 15, a B water inlet branch pipe 16 and a backwashing pipeline 17, the A water inlet branch pipe 15 is provided with a B valve 18, the B water inlet branch pipe 16 is provided with a C valve 19, the backwashing pipeline 17 is provided with a D valve 20, the bottom of the water outlet well 13 is provided with a lifting pump 21, and the backwashing pipeline 17 is connected with the lifting pump 21; dividing the sewage into two parts, wherein one part directly enters the vertical-flow artificial wetland, the other part directly enters the bottom of the horizontal subsurface-flow artificial wetland to carry out denitrification reaction with the nitrifying liquid, the water inlet channel 50 mixes the sewage between the vertical-flow artificial wetland 11 and the horizontal subsurface-flow artificial wetland 12, and the backwashing pipeline 17 carries out backwashing treatment on the high-efficiency composite-flow artificial wetland 3; the upper part of the vertical flow artificial wetland 11 is provided with an A water distribution perforated pipe 22, a plurality of A water distribution holes 23 are distributed on the A water distribution perforated pipe 22 at equal intervals, the aperture of the A water distribution holes 23 is 10mm, the lower part of the vertical flow artificial wetland 11 is provided with an A inverted film perforated pipe 24, a plurality of A inverted film holes 25 are distributed on the A inverted film perforated pipe 24 at equal intervals, and the aperture of the A inverted film holes 25 is 20 mm; the A water distribution perforated pipe 22 performs water distribution treatment on the vertical flow artificial wetland 11, and the A inverted film perforated pipe 24 performs dredging treatment on the vertical flow artificial wetland 11.
Embodiment 5 of the utility model: a high-efficiency composite flow constructed wetland system comprises a grid regulating tank 1, a full-automatic backwashing filter 2, a high-efficiency composite flow constructed wetland 3, an A pipeline 4 and a B pipeline 5, wherein the grid regulating tank 1 is connected with the full-automatic backwashing filter 2 through the A pipeline 4, and the full-automatic backwashing filter 2 is connected with the high-efficiency composite flow constructed wetland 3 through the B pipeline 5; the sediments, the trapped matters and the peeled biological membranes generated in the wetland operation process are discharged out of the wetland unit at regular intervals, so that the water flow in the wetland is ensured to be smooth; the grid adjusting tank 1 comprises a grid well 6 and a hydrolysis acidification adjusting tank 7, the grid well 6 is connected with the hydrolysis acidification adjusting tank 7, an elastic three-dimensional filler 8 and a water inlet pump 9 are arranged in the hydrolysis acidification adjusting tank 7, the water inlet pump 9 is connected with the pipeline A4, and the pipeline A4 is provided with a valve A10; the elastic three-dimensional filler 8 intercepts and adsorbs small particles, decomposes macromolecular organic matters into small molecules convenient for oxidation treatment, removes partial organic matters, improves the biodegradability of wetland inlet water, and ensures that the outlet water has no bad smell of anaerobic fermentation and does not influence the surrounding environment; the high-efficiency composite flow artificial wetland 3 comprises a vertical flow artificial wetland 11, a horizontal subsurface flow artificial wetland 12, a water outlet well 13 and a membrane pouring well 14, wherein a water inlet channel 50 is arranged between the vertical flow artificial wetland 11 and the horizontal subsurface flow artificial wetland 12, the water inlet channel 50 is arranged on the side wall of the bottom of the vertical flow artificial wetland 11, the B pipeline 5 comprises an A water inlet branch pipe 15, a B water inlet branch pipe 16 and a backwashing pipeline 17, the A water inlet branch pipe 15 is provided with a B valve 18, the B water inlet branch pipe 16 is provided with a C valve 19, the backwashing pipeline 17 is provided with a D valve 20, the bottom of the water outlet well 13 is provided with a lifting pump 21, and the backwashing pipeline 17 is connected with the lifting pump 21; dividing the sewage into two parts, wherein one part directly enters the vertical-flow artificial wetland, the other part directly enters the bottom of the horizontal subsurface-flow artificial wetland to carry out denitrification reaction with the nitrifying liquid, the water inlet channel 50 mixes the sewage between the vertical-flow artificial wetland 11 and the horizontal subsurface-flow artificial wetland 12, and the backwashing pipeline 17 carries out backwashing treatment on the high-efficiency composite-flow artificial wetland 3; the upper part of the vertical flow artificial wetland 11 is provided with an A water distribution perforated pipe 22, a plurality of A water distribution holes 23 are distributed on the A water distribution perforated pipe 22 at equal intervals, the aperture of the A water distribution holes 23 is 10mm, the lower part of the vertical flow artificial wetland 11 is provided with an A inverted film perforated pipe 24, a plurality of A inverted film holes 25 are distributed on the A inverted film perforated pipe 24 at equal intervals, and the aperture of the A inverted film holes 25 is 20 mm; the A water distribution perforated pipe 22 is used for carrying out water distribution treatment on the vertical flow artificial wetland 11, and the A inverted film perforated pipe 24 is used for carrying out desilting treatment on the vertical flow artificial wetland 11; the horizontal subsurface flow constructed wetland 12 is internally provided with an A clapboard 26 and a B clapboard 27, the left side of the A clapboard 26 is connected with the inner wall of the horizontal subsurface flow constructed wetland 12, the distance between the right side of the A clapboard 26 and the inner wall of the horizontal subsurface flow constructed wetland 12 is D1, the right side of the B clapboard 27 is connected with the inner wall of the horizontal subsurface flow constructed wetland 12, the distance between the left side of the B clapboard 27 and the inner wall of the horizontal subsurface flow constructed wetland 12 is D2, D1 is D2, the A clapboard 26 is arranged below the B clapboard 27, a water inlet channel 50 is arranged below the A clapboard 26, a water collecting perforated pipe 28 is arranged above the B clapboard 27, the water collecting perforated pipe 28 is connected with a water outlet well 13, a plurality of water collecting holes 29 are distributed on the water collecting perforated pipe 28 at equal intervals, the aperture of the water collecting holes 29 is 15mm, the lower part of the horizontal subsurface flow constructed wetland 12 is provided with a B water distributing perforated pipe 30 and a B inverted water distributing perforated pipe 31, the water distribution perforated pipe 30 and the inverted film perforated pipe 31B are both arranged below the baffle plate 27B, a plurality of water distribution holes 32B are distributed on the water distribution perforated pipe 30B at equal intervals, the aperture of the water distribution holes 32B is 10mm, a plurality of inverted film holes 33B are distributed on the inverted film perforated pipe 31B at equal intervals, and the aperture of the inverted film holes 33B is 20 mm; a partition plate 26 and a partition plate 27 are arranged in the horizontal subsurface flow constructed wetland and are designed into a horizontal baffle plate flow form, the vertical flow constructed wetland 11 realizes natural oxygenation by forming flooding and drying conditions of the wetland through periodic water inlet and outlet, fully nitrifies organic matters and then enters the horizontal subsurface flow constructed wetland 12, an aerobic and anaerobic environment is formed through design of a folded plate of horizontal flow, the nitrification and denitrification effects are enhanced, the nitrogen and phosphorus removal effect of the whole system is improved, a water distribution perforated pipe 30 performs water distribution treatment on the horizontal subsurface flow constructed wetland 12, and a reverse membrane perforated pipe 31 performs desilting treatment on the horizontal subsurface flow constructed wetland 12.
Embodiment 6 of the utility model: a high-efficiency composite flow constructed wetland system comprises a grid regulating tank 1, a full-automatic backwashing filter 2, a high-efficiency composite flow constructed wetland 3, an A pipeline 4 and a B pipeline 5, wherein the grid regulating tank 1 is connected with the full-automatic backwashing filter 2 through the A pipeline 4, and the full-automatic backwashing filter 2 is connected with the high-efficiency composite flow constructed wetland 3 through the B pipeline 5; the sediments, the trapped matters and the peeled biological membranes generated in the wetland operation process are discharged out of the wetland unit at regular intervals, so that the water flow in the wetland is ensured to be smooth; the grid adjusting tank 1 comprises a grid well 6 and a hydrolysis acidification adjusting tank 7, the grid well 6 is connected with the hydrolysis acidification adjusting tank 7, an elastic three-dimensional filler 8 and a water inlet pump 9 are arranged in the hydrolysis acidification adjusting tank 7, the water inlet pump 9 is connected with the pipeline A4, and the pipeline A4 is provided with a valve A10; the elastic three-dimensional filler 8 intercepts and adsorbs small particles, decomposes macromolecular organic matters into small molecules convenient for oxidation treatment, removes partial organic matters, improves the biodegradability of wetland inlet water, and ensures that the outlet water has no bad smell of anaerobic fermentation and does not influence the surrounding environment; the high-efficiency composite flow artificial wetland 3 comprises a vertical flow artificial wetland 11, a horizontal subsurface flow artificial wetland 12, a water outlet well 13 and a membrane pouring well 14, wherein a water inlet channel 50 is arranged between the vertical flow artificial wetland 11 and the horizontal subsurface flow artificial wetland 12, the water inlet channel 50 is arranged on the side wall of the bottom of the vertical flow artificial wetland 11, the B pipeline 5 comprises an A water inlet branch pipe 15, a B water inlet branch pipe 16 and a backwashing pipeline 17, the A water inlet branch pipe 15 is provided with a B valve 18, the B water inlet branch pipe 16 is provided with a C valve 19, the backwashing pipeline 17 is provided with a D valve 20, the bottom of the water outlet well 13 is provided with a lifting pump 21, and the backwashing pipeline 17 is connected with the lifting pump 21; dividing the sewage into two parts, wherein one part directly enters the vertical-flow artificial wetland, the other part directly enters the bottom of the horizontal subsurface-flow artificial wetland to carry out denitrification reaction with the nitrifying liquid, the water inlet channel 50 mixes the sewage between the vertical-flow artificial wetland 11 and the horizontal subsurface-flow artificial wetland 12, and the backwashing pipeline 17 carries out backwashing treatment on the high-efficiency composite-flow artificial wetland 3; the upper part of the vertical flow artificial wetland 11 is provided with an A water distribution perforated pipe 22, a plurality of A water distribution holes 23 are distributed on the A water distribution perforated pipe 22 at equal intervals, the aperture of the A water distribution holes 23 is 10mm, the lower part of the vertical flow artificial wetland 11 is provided with an A inverted film perforated pipe 24, a plurality of A inverted film holes 25 are distributed on the A inverted film perforated pipe 24 at equal intervals, and the aperture of the A inverted film holes 25 is 20 mm; the A water distribution perforated pipe 22 is used for carrying out water distribution treatment on the vertical flow artificial wetland 11, and the A inverted film perforated pipe 24 is used for carrying out desilting treatment on the vertical flow artificial wetland 11; the horizontal subsurface flow constructed wetland 12 is internally provided with an A clapboard 26 and a B clapboard 27, the left side of the A clapboard 26 is connected with the inner wall of the horizontal subsurface flow constructed wetland 12, the distance between the right side of the A clapboard 26 and the inner wall of the horizontal subsurface flow constructed wetland 12 is D1, the right side of the B clapboard 27 is connected with the inner wall of the horizontal subsurface flow constructed wetland 12, the distance between the left side of the B clapboard 27 and the inner wall of the horizontal subsurface flow constructed wetland 12 is D2, D1 is D2, the A clapboard 26 is arranged below the B clapboard 27, a water inlet channel 50 is arranged below the A clapboard 26, a water collecting perforated pipe 28 is arranged above the B clapboard 27, the water collecting perforated pipe 28 is connected with a water outlet well 13, a plurality of water collecting holes 29 are distributed on the water collecting perforated pipe 28 at equal intervals, the aperture of the water collecting holes 29 is 15mm, the lower part of the horizontal subsurface flow constructed wetland 12 is provided with a B water distributing perforated pipe 30 and a B inverted water distributing perforated pipe 31, the water distribution perforated pipe 30 and the inverted film perforated pipe 31B are both arranged below the baffle plate 27B, a plurality of water distribution holes 32B are distributed on the water distribution perforated pipe 30B at equal intervals, the aperture of the water distribution holes 32B is 10mm, a plurality of inverted film holes 33B are distributed on the inverted film perforated pipe 31B at equal intervals, and the aperture of the inverted film holes 33B is 20 mm; the horizontal subsurface flow constructed wetland is internally provided with an A clapboard 26 and a B clapboard 27 which are designed into a horizontal baffle flow form, the vertical flow constructed wetland 11 realizes natural oxygenation by forming flooding and drying conditions of the wetland by periodically feeding and discharging water, fully nitrifies organic matters and then enters the horizontal subsurface flow constructed wetland 12, an aerobic and anaerobic environment is formed by designing a horizontal flow folded plate, the nitrification and denitrification effects are enhanced, the integral nitrogen and phosphorus removal effect of the system is improved, a B water distribution perforated pipe 30 performs water distribution treatment on the horizontal subsurface flow constructed wetland 12, and a B inverted film perforated pipe 31 performs desilting treatment on the horizontal subsurface flow constructed wetland 12; a vertical flow wetland planting layer 34 is arranged in the vertical flow wetland 11, a horizontal subsurface flow wetland planting layer 35 is arranged in the horizontal subsurface flow wetland 12, a coarse sand layer 36 with the thickness of 100mm, a gravel layer 37 with the thickness of 500mm, a zeolite layer 38 with the thickness of 500mm, a coarse sand layer 36 with the thickness of 200mm and planting soil 39 with the thickness of 200mm are sequentially arranged on the vertical flow wetland planting layer 34 from bottom to top, the coarse sand layer 36 with the thickness of 100mm, a blast furnace slag layer 40 with the thickness of 400mm, a dolomite layer 41 with the thickness of 400mm, the coarse sand layer 36 with the thickness of 200mm and the planting soil 39 with the thickness of 200mm are sequentially arranged on the horizontal subsurface flow wetland planting layer 35 from bottom to top, a plurality of plants 42 are arranged on the planting soil 39 at equal intervals, the particle size of coarse sand in the coarse sand layer 36 is 0.9-1.2mm, the particle size of gravel in the gravel layer 37 is 80-120mm, and the particle size of zeolite in the zeolite layer 38 is 20-60mm, the grain size of the blast furnace slag in the blast furnace slag layer 40 is 80-120mm, and the grain size of the dolomite in the dolomite layer 41 is 15-60 mm.
Embodiment 7 of the utility model: a high-efficiency composite flow constructed wetland system comprises a grid regulating tank 1, a full-automatic backwashing filter 2, a high-efficiency composite flow constructed wetland 3, an A pipeline 4 and a B pipeline 5, wherein the grid regulating tank 1 is connected with the full-automatic backwashing filter 2 through the A pipeline 4, and the full-automatic backwashing filter 2 is connected with the high-efficiency composite flow constructed wetland 3 through the B pipeline 5; the sediments, the trapped matters and the peeled biological membranes generated in the wetland operation process are discharged out of the wetland unit at regular intervals, so that the water flow in the wetland is ensured to be smooth; the grid adjusting tank 1 comprises a grid well 6 and a hydrolysis acidification adjusting tank 7, the grid well 6 is connected with the hydrolysis acidification adjusting tank 7, an elastic three-dimensional filler 8 and a water inlet pump 9 are arranged in the hydrolysis acidification adjusting tank 7, the water inlet pump 9 is connected with the pipeline A4, and the pipeline A4 is provided with a valve A10; the elastic three-dimensional filler 8 intercepts and adsorbs small particles, decomposes macromolecular organic matters into small molecules convenient for oxidation treatment, removes partial organic matters, improves the biodegradability of wetland inlet water, and ensures that the outlet water has no bad smell of anaerobic fermentation and does not influence the surrounding environment; the high-efficiency composite flow artificial wetland 3 comprises a vertical flow artificial wetland 11, a horizontal subsurface flow artificial wetland 12, a water outlet well 13 and a membrane pouring well 14, wherein a water inlet channel 50 is arranged between the vertical flow artificial wetland 11 and the horizontal subsurface flow artificial wetland 12, the water inlet channel 50 is arranged on the side wall of the bottom of the vertical flow artificial wetland 11, the B pipeline 5 comprises an A water inlet branch pipe 15, a B water inlet branch pipe 16 and a backwashing pipeline 17, the A water inlet branch pipe 15 is provided with a B valve 18, the B water inlet branch pipe 16 is provided with a C valve 19, the backwashing pipeline 17 is provided with a D valve 20, the bottom of the water outlet well 13 is provided with a lifting pump 21, and the backwashing pipeline 17 is connected with the lifting pump 21; dividing the sewage into two parts, wherein one part directly enters the vertical-flow artificial wetland, the other part directly enters the bottom of the horizontal subsurface-flow artificial wetland to carry out denitrification reaction with the nitrifying liquid, the water inlet channel 50 mixes the sewage between the vertical-flow artificial wetland 11 and the horizontal subsurface-flow artificial wetland 12, and the backwashing pipeline 17 carries out backwashing treatment on the high-efficiency composite-flow artificial wetland 3; the upper part of the vertical flow artificial wetland 11 is provided with an A water distribution perforated pipe 22, a plurality of A water distribution holes 23 are distributed on the A water distribution perforated pipe 22 at equal intervals, the aperture of the A water distribution holes 23 is 10mm, the lower part of the vertical flow artificial wetland 11 is provided with an A inverted film perforated pipe 24, a plurality of A inverted film holes 25 are distributed on the A inverted film perforated pipe 24 at equal intervals, and the aperture of the A inverted film holes 25 is 20 mm; the A water distribution perforated pipe 22 is used for carrying out water distribution treatment on the vertical flow artificial wetland 11, and the A inverted film perforated pipe 24 is used for carrying out desilting treatment on the vertical flow artificial wetland 11; the horizontal subsurface flow constructed wetland 12 is internally provided with an A clapboard 26 and a B clapboard 27, the left side of the A clapboard 26 is connected with the inner wall of the horizontal subsurface flow constructed wetland 12, the distance between the right side of the A clapboard 26 and the inner wall of the horizontal subsurface flow constructed wetland 12 is D1, the right side of the B clapboard 27 is connected with the inner wall of the horizontal subsurface flow constructed wetland 12, the distance between the left side of the B clapboard 27 and the inner wall of the horizontal subsurface flow constructed wetland 12 is D2, D1 is D2, the A clapboard 26 is arranged below the B clapboard 27, a water inlet channel 50 is arranged below the A clapboard 26, a water collecting perforated pipe 28 is arranged above the B clapboard 27, the water collecting perforated pipe 28 is connected with a water outlet well 13, a plurality of water collecting holes 29 are distributed on the water collecting perforated pipe 28 at equal intervals, the aperture of the water collecting holes 29 is 15mm, the lower part of the horizontal subsurface flow constructed wetland 12 is provided with a B water distributing perforated pipe 30 and a B inverted water distributing perforated pipe 31, the water distribution perforated pipe 30 and the inverted film perforated pipe 31B are both arranged below the baffle plate 27B, a plurality of water distribution holes 32B are distributed on the water distribution perforated pipe 30B at equal intervals, the aperture of the water distribution holes 32B is 10mm, a plurality of inverted film holes 33B are distributed on the inverted film perforated pipe 31B at equal intervals, and the aperture of the inverted film holes 33B is 20 mm; the horizontal subsurface flow constructed wetland is internally provided with an A clapboard 26 and a B clapboard 27 which are designed into a horizontal baffle flow form, the vertical flow constructed wetland 11 realizes natural oxygenation by forming flooding and drying conditions of the wetland by periodically feeding and discharging water, fully nitrifies organic matters and then enters the horizontal subsurface flow constructed wetland 12, an aerobic and anaerobic environment is formed by designing a horizontal flow folded plate, the nitrification and denitrification effects are enhanced, the integral nitrogen and phosphorus removal effect of the system is improved, a B water distribution perforated pipe 30 performs water distribution treatment on the horizontal subsurface flow constructed wetland 12, and a B inverted film perforated pipe 31 performs desilting treatment on the horizontal subsurface flow constructed wetland 12; a vertical flow wetland planting layer 34 is arranged in the vertical flow wetland 11, a horizontal subsurface flow wetland planting layer 35 is arranged in the horizontal subsurface flow wetland 12, a coarse sand layer 36 with the thickness of 100mm, a gravel layer 37 with the thickness of 500mm, a zeolite layer 38 with the thickness of 500mm, a coarse sand layer 36 with the thickness of 200mm and planting soil 39 with the thickness of 200mm are sequentially arranged on the vertical flow wetland planting layer 34 from bottom to top, the coarse sand layer 36 with the thickness of 100mm, a blast furnace slag layer 40 with the thickness of 400mm, a dolomite layer 41 with the thickness of 400mm, the coarse sand layer 36 with the thickness of 200mm and the planting soil 39 with the thickness of 200mm are sequentially arranged on the horizontal subsurface flow wetland planting layer 35 from bottom to top, a plurality of plants 42 are arranged on the planting soil 39 at equal intervals, the particle size of coarse sand in the coarse sand layer 36 is 0.9-1.2mm, the particle size of gravel in the gravel layer 37 is 80-120mm, and the particle size of zeolite in the zeolite layer 38 is 20-60mm, the grain size of the blast furnace slag in the blast furnace slag layer 40 is 80-120mm, and the grain size of the dolomite in the dolomite layer 41 is 15-60 mm; the A water distribution perforated pipe 22 is connected with the A water inlet branch pipe 15, the A film pouring perforated pipe 24 is in pipeline connection with the film pouring well 14, and an E valve 43 is arranged on a pipe section between the A film pouring perforated pipe 24 and the film pouring well 14.
Embodiment 8 of the utility model: a high-efficiency composite flow constructed wetland system comprises a grid regulating tank 1, a full-automatic backwashing filter 2, a high-efficiency composite flow constructed wetland 3, an A pipeline 4 and a B pipeline 5, wherein the grid regulating tank 1 is connected with the full-automatic backwashing filter 2 through the A pipeline 4, and the full-automatic backwashing filter 2 is connected with the high-efficiency composite flow constructed wetland 3 through the B pipeline 5; the sediments, the trapped matters and the peeled biological membranes generated in the wetland operation process are discharged out of the wetland unit at regular intervals, so that the water flow in the wetland is ensured to be smooth; the grid adjusting tank 1 comprises a grid well 6 and a hydrolysis acidification adjusting tank 7, the grid well 6 is connected with the hydrolysis acidification adjusting tank 7, an elastic three-dimensional filler 8 and a water inlet pump 9 are arranged in the hydrolysis acidification adjusting tank 7, the water inlet pump 9 is connected with the pipeline A4, and the pipeline A4 is provided with a valve A10; the elastic three-dimensional filler 8 intercepts and adsorbs small particles, decomposes macromolecular organic matters into small molecules convenient for oxidation treatment, removes partial organic matters, improves the biodegradability of wetland inlet water, and ensures that the outlet water has no bad smell of anaerobic fermentation and does not influence the surrounding environment; the high-efficiency composite flow artificial wetland 3 comprises a vertical flow artificial wetland 11, a horizontal subsurface flow artificial wetland 12, a water outlet well 13 and a membrane pouring well 14, wherein a water inlet channel 50 is arranged between the vertical flow artificial wetland 11 and the horizontal subsurface flow artificial wetland 12, the water inlet channel 50 is arranged on the side wall of the bottom of the vertical flow artificial wetland 11, the B pipeline 5 comprises an A water inlet branch pipe 15, a B water inlet branch pipe 16 and a backwashing pipeline 17, the A water inlet branch pipe 15 is provided with a B valve 18, the B water inlet branch pipe 16 is provided with a C valve 19, the backwashing pipeline 17 is provided with a D valve 20, the bottom of the water outlet well 13 is provided with a lifting pump 21, and the backwashing pipeline 17 is connected with the lifting pump 21; dividing the sewage into two parts, wherein one part directly enters the vertical-flow artificial wetland, the other part directly enters the bottom of the horizontal subsurface-flow artificial wetland to carry out denitrification reaction with the nitrifying liquid, the water inlet channel 50 mixes the sewage between the vertical-flow artificial wetland 11 and the horizontal subsurface-flow artificial wetland 12, and the backwashing pipeline 17 carries out backwashing treatment on the high-efficiency composite-flow artificial wetland 3; the upper part of the vertical flow artificial wetland 11 is provided with an A water distribution perforated pipe 22, a plurality of A water distribution holes 23 are distributed on the A water distribution perforated pipe 22 at equal intervals, the aperture of the A water distribution holes 23 is 10mm, the lower part of the vertical flow artificial wetland 11 is provided with an A inverted film perforated pipe 24, a plurality of A inverted film holes 25 are distributed on the A inverted film perforated pipe 24 at equal intervals, and the aperture of the A inverted film holes 25 is 20 mm; the A water distribution perforated pipe 22 is used for carrying out water distribution treatment on the vertical flow artificial wetland 11, and the A inverted film perforated pipe 24 is used for carrying out desilting treatment on the vertical flow artificial wetland 11; the horizontal subsurface flow constructed wetland 12 is internally provided with an A clapboard 26 and a B clapboard 27, the left side of the A clapboard 26 is connected with the inner wall of the horizontal subsurface flow constructed wetland 12, the distance between the right side of the A clapboard 26 and the inner wall of the horizontal subsurface flow constructed wetland 12 is D1, the right side of the B clapboard 27 is connected with the inner wall of the horizontal subsurface flow constructed wetland 12, the distance between the left side of the B clapboard 27 and the inner wall of the horizontal subsurface flow constructed wetland 12 is D2, D1 is D2, the A clapboard 26 is arranged below the B clapboard 27, a water inlet channel 50 is arranged below the A clapboard 26, a water collecting perforated pipe 28 is arranged above the B clapboard 27, the water collecting perforated pipe 28 is connected with a water outlet well 13, a plurality of water collecting holes 29 are distributed on the water collecting perforated pipe 28 at equal intervals, the aperture of the water collecting holes 29 is 15mm, the lower part of the horizontal subsurface flow constructed wetland 12 is provided with a B water distributing perforated pipe 30 and a B inverted water distributing perforated pipe 31, the water distribution perforated pipe 30 and the inverted film perforated pipe 31B are both arranged below the baffle plate 27B, a plurality of water distribution holes 32B are distributed on the water distribution perforated pipe 30B at equal intervals, the aperture of the water distribution holes 32B is 10mm, a plurality of inverted film holes 33B are distributed on the inverted film perforated pipe 31B at equal intervals, and the aperture of the inverted film holes 33B is 20 mm; the horizontal subsurface flow constructed wetland is internally provided with an A clapboard 26 and a B clapboard 27 which are designed into a horizontal baffle flow form, the vertical flow constructed wetland 11 realizes natural oxygenation by forming flooding and drying conditions of the wetland by periodically feeding and discharging water, fully nitrifies organic matters and then enters the horizontal subsurface flow constructed wetland 12, an aerobic and anaerobic environment is formed by designing a horizontal flow folded plate, the nitrification and denitrification effects are enhanced, the integral nitrogen and phosphorus removal effect of the system is improved, a B water distribution perforated pipe 30 performs water distribution treatment on the horizontal subsurface flow constructed wetland 12, and a B inverted film perforated pipe 31 performs desilting treatment on the horizontal subsurface flow constructed wetland 12; a vertical flow wetland planting layer 34 is arranged in the vertical flow wetland 11, a horizontal subsurface flow wetland planting layer 35 is arranged in the horizontal subsurface flow wetland 12, a coarse sand layer 36 with the thickness of 100mm, a gravel layer 37 with the thickness of 500mm, a zeolite layer 38 with the thickness of 500mm, a coarse sand layer 36 with the thickness of 200mm and planting soil 39 with the thickness of 200mm are sequentially arranged on the vertical flow wetland planting layer 34 from bottom to top, the coarse sand layer 36 with the thickness of 100mm, a blast furnace slag layer 40 with the thickness of 400mm, a dolomite layer 41 with the thickness of 400mm, the coarse sand layer 36 with the thickness of 200mm and the planting soil 39 with the thickness of 200mm are sequentially arranged on the horizontal subsurface flow wetland planting layer 35 from bottom to top, a plurality of plants 42 are arranged on the planting soil 39 at equal intervals, the particle size of coarse sand in the coarse sand layer 36 is 0.9-1.2mm, the particle size of gravel in the gravel layer 37 is 80-120mm, and the particle size of zeolite in the zeolite layer 38 is 20-60mm, the grain size of the blast furnace slag in the blast furnace slag layer 40 is 80-120mm, and the grain size of the dolomite in the dolomite layer 41 is 15-60 mm; the A water distribution perforated pipe 22 is connected with the A water inlet branch pipe 15, the A film pouring perforated pipe 24 is in pipeline connection with the film pouring well 14, and an E valve 43 is arranged on a pipe section between the A film pouring perforated pipe 24 and the film pouring well 14; the water distribution perforated pipe B30 is connected with the water inlet branch pipe B16, the film pouring perforated pipe B31 is in pipeline connection with the film pouring well 14, and an F valve 44 is arranged on a pipe section between the film pouring perforated pipe B31 and the film pouring well 14.
Embodiment 9 of the utility model: a high-efficiency composite flow constructed wetland system comprises a grid regulating tank 1, a full-automatic backwashing filter 2, a high-efficiency composite flow constructed wetland 3, an A pipeline 4 and a B pipeline 5, wherein the grid regulating tank 1 is connected with the full-automatic backwashing filter 2 through the A pipeline 4, and the full-automatic backwashing filter 2 is connected with the high-efficiency composite flow constructed wetland 3 through the B pipeline 5; the sediments, the trapped matters and the peeled biological membranes generated in the wetland operation process are discharged out of the wetland unit at regular intervals, so that the water flow in the wetland is ensured to be smooth; the grid adjusting tank 1 comprises a grid well 6 and a hydrolysis acidification adjusting tank 7, the grid well 6 is connected with the hydrolysis acidification adjusting tank 7, an elastic three-dimensional filler 8 and a water inlet pump 9 are arranged in the hydrolysis acidification adjusting tank 7, the water inlet pump 9 is connected with the pipeline A4, and the pipeline A4 is provided with a valve A10; the elastic three-dimensional filler 8 intercepts and adsorbs small particles, decomposes macromolecular organic matters into small molecules convenient for oxidation treatment, removes partial organic matters, improves the biodegradability of wetland inlet water, and ensures that the outlet water has no bad smell of anaerobic fermentation and does not influence the surrounding environment; the high-efficiency composite flow artificial wetland 3 comprises a vertical flow artificial wetland 11, a horizontal subsurface flow artificial wetland 12, a water outlet well 13 and a membrane pouring well 14, wherein a water inlet channel 50 is arranged between the vertical flow artificial wetland 11 and the horizontal subsurface flow artificial wetland 12, the water inlet channel 50 is arranged on the side wall of the bottom of the vertical flow artificial wetland 11, the B pipeline 5 comprises an A water inlet branch pipe 15, a B water inlet branch pipe 16 and a backwashing pipeline 17, the A water inlet branch pipe 15 is provided with a B valve 18, the B water inlet branch pipe 16 is provided with a C valve 19, the backwashing pipeline 17 is provided with a D valve 20, the bottom of the water outlet well 13 is provided with a lifting pump 21, and the backwashing pipeline 17 is connected with the lifting pump 21; dividing the sewage into two parts, wherein one part directly enters the vertical-flow artificial wetland, the other part directly enters the bottom of the horizontal subsurface-flow artificial wetland to carry out denitrification reaction with the nitrifying liquid, the water inlet channel 50 mixes the sewage between the vertical-flow artificial wetland 11 and the horizontal subsurface-flow artificial wetland 12, and the backwashing pipeline 17 carries out backwashing treatment on the high-efficiency composite-flow artificial wetland 3; the upper part of the vertical flow artificial wetland 11 is provided with an A water distribution perforated pipe 22, a plurality of A water distribution holes 23 are distributed on the A water distribution perforated pipe 22 at equal intervals, the aperture of the A water distribution holes 23 is 10mm, the lower part of the vertical flow artificial wetland 11 is provided with an A inverted film perforated pipe 24, a plurality of A inverted film holes 25 are distributed on the A inverted film perforated pipe 24 at equal intervals, and the aperture of the A inverted film holes 25 is 20 mm; the A water distribution perforated pipe 22 is used for carrying out water distribution treatment on the vertical flow artificial wetland 11, and the A inverted film perforated pipe 24 is used for carrying out desilting treatment on the vertical flow artificial wetland 11; the horizontal subsurface flow constructed wetland 12 is internally provided with an A clapboard 26 and a B clapboard 27, the left side of the A clapboard 26 is connected with the inner wall of the horizontal subsurface flow constructed wetland 12, the distance between the right side of the A clapboard 26 and the inner wall of the horizontal subsurface flow constructed wetland 12 is D1, the right side of the B clapboard 27 is connected with the inner wall of the horizontal subsurface flow constructed wetland 12, the distance between the left side of the B clapboard 27 and the inner wall of the horizontal subsurface flow constructed wetland 12 is D2, D1 is D2, the A clapboard 26 is arranged below the B clapboard 27, a water inlet channel 50 is arranged below the A clapboard 26, a water collecting perforated pipe 28 is arranged above the B clapboard 27, the water collecting perforated pipe 28 is connected with a water outlet well 13, a plurality of water collecting holes 29 are distributed on the water collecting perforated pipe 28 at equal intervals, the aperture of the water collecting holes 29 is 15mm, the lower part of the horizontal subsurface flow constructed wetland 12 is provided with a B water distributing perforated pipe 30 and a B inverted water distributing perforated pipe 31, the water distribution perforated pipe 30 and the inverted film perforated pipe 31B are both arranged below the baffle plate 27B, a plurality of water distribution holes 32B are distributed on the water distribution perforated pipe 30B at equal intervals, the aperture of the water distribution holes 32B is 10mm, a plurality of inverted film holes 33B are distributed on the inverted film perforated pipe 31B at equal intervals, and the aperture of the inverted film holes 33B is 20 mm; the horizontal subsurface flow constructed wetland is internally provided with an A clapboard 26 and a B clapboard 27 which are designed into a horizontal baffle flow form, the vertical flow constructed wetland 11 realizes natural oxygenation by forming flooding and drying conditions of the wetland by periodically feeding and discharging water, fully nitrifies organic matters and then enters the horizontal subsurface flow constructed wetland 12, an aerobic and anaerobic environment is formed by designing a horizontal flow folded plate, the nitrification and denitrification effects are enhanced, the integral nitrogen and phosphorus removal effect of the system is improved, a B water distribution perforated pipe 30 performs water distribution treatment on the horizontal subsurface flow constructed wetland 12, and a B inverted film perforated pipe 31 performs desilting treatment on the horizontal subsurface flow constructed wetland 12; a vertical flow wetland planting layer 34 is arranged in the vertical flow wetland 11, a horizontal subsurface flow wetland planting layer 35 is arranged in the horizontal subsurface flow wetland 12, a coarse sand layer 36 with the thickness of 100mm, a gravel layer 37 with the thickness of 500mm, a zeolite layer 38 with the thickness of 500mm, a coarse sand layer 36 with the thickness of 200mm and planting soil 39 with the thickness of 200mm are sequentially arranged on the vertical flow wetland planting layer 34 from bottom to top, the coarse sand layer 36 with the thickness of 100mm, a blast furnace slag layer 40 with the thickness of 400mm, a dolomite layer 41 with the thickness of 400mm, the coarse sand layer 36 with the thickness of 200mm and the planting soil 39 with the thickness of 200mm are sequentially arranged on the horizontal subsurface flow wetland planting layer 35 from bottom to top, a plurality of plants 42 are arranged on the planting soil 39 at equal intervals, the particle size of coarse sand in the coarse sand layer 36 is 0.9-1.2mm, the particle size of gravel in the gravel layer 37 is 80-120mm, and the particle size of zeolite in the zeolite layer 38 is 20-60mm, the grain size of the blast furnace slag in the blast furnace slag layer 40 is 80-120mm, and the grain size of the dolomite in the dolomite layer 41 is 15-60 mm; the A water distribution perforated pipe 22 is connected with the A water inlet branch pipe 15, the A film pouring perforated pipe 24 is in pipeline connection with the film pouring well 14, and an E valve 43 is arranged on a pipe section between the A film pouring perforated pipe 24 and the film pouring well 14; the water distribution perforated pipe B30 is connected with the water inlet branch pipe B16, the film pouring perforated pipe B31 is in pipeline connection with the film pouring well 14, and an F valve 44 is arranged on a pipe section between the film pouring perforated pipe B31 and the film pouring well 14; a G valve 45 is arranged on a pipe section between the water collecting perforated pipe 28 and the water outlet well 13, a C pipe 46 and a D pipe 47 are arranged on a pipe section between the G valve 45 and the water collecting perforated pipe 28, an H valve 48 is arranged on the C pipe 46, an I valve 49 is arranged on the D pipe 47, one end of the D pipe 47 is connected to the pipe section between the G valve 45 and the water collecting perforated pipe 28, and the other end of the D pipe 47 is connected to the pipe section between the D valve 20 and the lift pump 21; the G valve 45 and the H valve 48 are adjusted to open according to different levels of the water outlet well 13, when the water inflow is large, the H valve 48 is opened, and when the water inflow is small, the G valve 45 is opened.
Embodiment 10 of the present invention: a high-efficiency composite flow constructed wetland system comprises a grid regulating tank 1, a full-automatic backwashing filter 2, a high-efficiency composite flow constructed wetland 3, an A pipeline 4 and a B pipeline 5, wherein the grid regulating tank 1 is connected with the full-automatic backwashing filter 2 through the A pipeline 4, and the full-automatic backwashing filter 2 is connected with the high-efficiency composite flow constructed wetland 3 through the B pipeline 5; the sediments, the trapped matters and the peeled biological membranes generated in the wetland operation process are discharged out of the wetland unit at regular intervals, so that the water flow in the wetland is ensured to be smooth; the grid adjusting tank 1 comprises a grid well 6 and a hydrolysis acidification adjusting tank 7, the grid well 6 is connected with the hydrolysis acidification adjusting tank 7, an elastic three-dimensional filler 8 and a water inlet pump 9 are arranged in the hydrolysis acidification adjusting tank 7, the water inlet pump 9 is connected with the pipeline A4, and the pipeline A4 is provided with a valve A10; the elastic three-dimensional filler 8 intercepts and adsorbs small particles, decomposes macromolecular organic matters into small molecules convenient for oxidation treatment, removes partial organic matters, improves the biodegradability of wetland inlet water, and ensures that the outlet water has no bad smell of anaerobic fermentation and does not influence the surrounding environment; the high-efficiency composite flow artificial wetland 3 comprises a vertical flow artificial wetland 11, a horizontal subsurface flow artificial wetland 12, a water outlet well 13 and a membrane pouring well 14, wherein a water inlet channel 50 is arranged between the vertical flow artificial wetland 11 and the horizontal subsurface flow artificial wetland 12, the water inlet channel 50 is arranged on the side wall of the bottom of the vertical flow artificial wetland 11, the B pipeline 5 comprises an A water inlet branch pipe 15, a B water inlet branch pipe 16 and a backwashing pipeline 17, the A water inlet branch pipe 15 is provided with a B valve 18, the B water inlet branch pipe 16 is provided with a C valve 19, the backwashing pipeline 17 is provided with a D valve 20, the bottom of the water outlet well 13 is provided with a lifting pump 21, and the backwashing pipeline 17 is connected with the lifting pump 21; dividing the sewage into two parts, wherein one part directly enters the vertical-flow artificial wetland, the other part directly enters the bottom of the horizontal subsurface-flow artificial wetland to carry out denitrification reaction with the nitrifying liquid, the water inlet channel 50 mixes the sewage between the vertical-flow artificial wetland 11 and the horizontal subsurface-flow artificial wetland 12, and the backwashing pipeline 17 carries out backwashing treatment on the high-efficiency composite-flow artificial wetland 3; the upper part of the vertical flow artificial wetland 11 is provided with an A water distribution perforated pipe 22, a plurality of A water distribution holes 23 are distributed on the A water distribution perforated pipe 22 at equal intervals, the aperture of the A water distribution holes 23 is 10mm, the lower part of the vertical flow artificial wetland 11 is provided with an A inverted film perforated pipe 24, a plurality of A inverted film holes 25 are distributed on the A inverted film perforated pipe 24 at equal intervals, and the aperture of the A inverted film holes 25 is 20 mm; the A water distribution perforated pipe 22 is used for carrying out water distribution treatment on the vertical flow artificial wetland 11, and the A inverted film perforated pipe 24 is used for carrying out desilting treatment on the vertical flow artificial wetland 11; the horizontal subsurface flow constructed wetland 12 is internally provided with an A clapboard 26 and a B clapboard 27, the left side of the A clapboard 26 is connected with the inner wall of the horizontal subsurface flow constructed wetland 12, the distance between the right side of the A clapboard 26 and the inner wall of the horizontal subsurface flow constructed wetland 12 is D1, the right side of the B clapboard 27 is connected with the inner wall of the horizontal subsurface flow constructed wetland 12, the distance between the left side of the B clapboard 27 and the inner wall of the horizontal subsurface flow constructed wetland 12 is D2, D1 is D2, the A clapboard 26 is arranged below the B clapboard 27, a water inlet channel 50 is arranged below the A clapboard 26, a water collecting perforated pipe 28 is arranged above the B clapboard 27, the water collecting perforated pipe 28 is connected with a water outlet well 13, a plurality of water collecting holes 29 are distributed on the water collecting perforated pipe 28 at equal intervals, the aperture of the water collecting holes 29 is 15mm, the lower part of the horizontal subsurface flow constructed wetland 12 is provided with a B water distributing perforated pipe 30 and a B inverted water distributing perforated pipe 31, the water distribution perforated pipe 30 and the inverted film perforated pipe 31B are both arranged below the baffle plate 27B, a plurality of water distribution holes 32B are distributed on the water distribution perforated pipe 30B at equal intervals, the aperture of the water distribution holes 32B is 10mm, a plurality of inverted film holes 33B are distributed on the inverted film perforated pipe 31B at equal intervals, and the aperture of the inverted film holes 33B is 20 mm; the horizontal subsurface flow constructed wetland is internally provided with an A clapboard 26 and a B clapboard 27 which are designed into a horizontal baffle flow form, the vertical flow constructed wetland 11 realizes natural oxygenation by forming flooding and drying conditions of the wetland by periodically feeding and discharging water, fully nitrifies organic matters and then enters the horizontal subsurface flow constructed wetland 12, an aerobic and anaerobic environment is formed by designing a horizontal flow folded plate, the nitrification and denitrification effects are enhanced, the integral nitrogen and phosphorus removal effect of the system is improved, a B water distribution perforated pipe 30 performs water distribution treatment on the horizontal subsurface flow constructed wetland 12, and a B inverted film perforated pipe 31 performs desilting treatment on the horizontal subsurface flow constructed wetland 12; a vertical flow wetland planting layer 34 is arranged in the vertical flow artificial wetland 11, a horizontal subsurface flow wetland planting layer 35 is arranged in the horizontal subsurface flow artificial wetland 12, a coarse sand layer 36 with the thickness of 100mm, a gravel layer 37 with the thickness of 500mm, a zeolite layer 38 with the thickness of 500mm, a coarse sand layer 36 with the thickness of 200mm and planting soil 39 with the thickness of 200mm are sequentially arranged on the vertical flow wetland planting layer 34 from bottom to top, a coarse sand layer 36 with the thickness of 100mm, a blast furnace slag layer 40 with the thickness of 400mm, a dolomite layer 41 with the thickness of 400mm, a plurality of plants 42 with the thickness of 200mm and planting soil 39 with the thickness of 200mm are sequentially arranged on the horizontal subsurface flow wetland planting layer 35 from bottom to top, the particle size of coarse sand in the coarse sand layer 36 is 0.9-1.2mm, preferably 1.1mm, the particle size of gravel in the gravel layer 37 is 80-120mm, preferably 100mm, the zeolite in the zeolite layer 38 has a particle size of 20-60mm, preferably 40mm, the blast furnace slag in the blast furnace slag layer 40 has a particle size of 80-120mm, preferably 100mm, and the dolomite in the dolomite layer 41 has a particle size of 15-60mm, preferably 45 mm; the A water distribution perforated pipe 22 is connected with the A water inlet branch pipe 15, the A film pouring perforated pipe 24 is in pipeline connection with the film pouring well 14, and an E valve 43 is arranged on a pipe section between the A film pouring perforated pipe 24 and the film pouring well 14; the water distribution perforated pipe B30 is connected with the water inlet branch pipe B16, the film pouring perforated pipe B31 is in pipeline connection with the film pouring well 14, and an F valve 44 is arranged on a pipe section between the film pouring perforated pipe B31 and the film pouring well 14; a G valve 45 is arranged on a pipe section between the water collecting perforated pipe 28 and the water outlet well 13, a C pipe 46 and a D pipe 47 are arranged on a pipe section between the G valve 45 and the water collecting perforated pipe 28, an H valve 48 is arranged on the C pipe 46, an I valve 49 is arranged on the D pipe 47, one end of the D pipe 47 is connected to the pipe section between the G valve 45 and the water collecting perforated pipe 28, and the other end of the D pipe 47 is connected to the pipe section between the D valve 20 and the lift pump 21; the G valve 45 and the H valve 48 are adjusted to open according to different levels of the water outlet well 13, when the water inflow is large, the H valve 48 is opened, and when the water inflow is small, the G valve 45 is opened.
The utility model discloses a theory of operation of embodiment: when the utility model works, the sewage in the grid well 6 enters the hydrolytic acidification regulating tank 7 for hydrolytic acidification treatment, and the retention time is 3-5 h; opening the valve A10, and conveying the sewage subjected to hydrolytic acidification treatment to the full-automatic backwashing filter 2 through the pipeline A4 by the water inlet pump 9 for filtering treatment; opening a valve B18, enabling the filtered sewage to enter a water distribution perforated pipe A22 through a water inlet branch pipe A15, enabling a water distribution hole A23 to convey the filtered sewage to a vertical flow wetland planting layer 34, opening a valve C19, enabling the filtered sewage to enter a water distribution perforated pipe B30 through a water inlet branch pipe B16, and enabling the water distribution hole A23 to convey the filtered sewage to a horizontal subsurface flow wetland planting layer 35; the sewage in the vertical flow artificial wetland 11 permeates from top to bottom through the vertical flow wetland planting layer 34, after partial organic matters, SS and complete nitrification are removed, the removed partial organic matters, SS and complete nitrification sewage enter the lower part of the horizontal subsurface flow artificial wetland 12 through the water inlet channel 50, the removed partial organic matters, SS and complete nitrification sewage are mixed with the untreated sewage conveyed by the water inlet branch pipe 16B, and then the sewage forms reciprocating flow through the partition boards A26 and the partition boards B27, so that aerobic and anoxic environments are formed alternately, and the denitrification effect of the sewage is realized. The removal of phosphorus in the sewage is completed through the horizontal subsurface flow wetland planting layer 35. Finally, after the sewage is collected by the water collecting perforated pipe 28, opening a G valve 45 and an H valve 48 to ensure that the sewage after phosphorus removal enters the water outlet well 13 for discharging; after the high-efficiency composite flow constructed wetland 3 runs for 60-75 days, dredging treatment is required; closing the valve B18 and the valve C19, the valve G45 and the valve H48, and simultaneously opening the valve D20 and the valve I49, when the filler in the high-efficiency subsurface flow constructed wetland 3 is submerged by the inflow water, closing the lift pump 21, the valve D20 and the valve I49 in the water outlet well 13, and after the filler is fully infiltrated, opening the valve E43 and the valve F44 in the water outlet well 14 for dredging treatment to ensure that the water flow in the wetland is smooth; after the flushing is finished, the valve E43 and the valve F44 are closed, the water inlet pump 9 and the valve B18 and the valve C19 on the water inlet pipeline are opened again, and the high-efficiency subsurface flow constructed wetland 3 works normally.