WO2024239407A1 - 一种阻水透气间歇曝气的模块式人工湿地 - Google Patents
一种阻水透气间歇曝气的模块式人工湿地 Download PDFInfo
- Publication number
- WO2024239407A1 WO2024239407A1 PCT/CN2023/101444 CN2023101444W WO2024239407A1 WO 2024239407 A1 WO2024239407 A1 WO 2024239407A1 CN 2023101444 W CN2023101444 W CN 2023101444W WO 2024239407 A1 WO2024239407 A1 WO 2024239407A1
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- WO
- WIPO (PCT)
- Prior art keywords
- water
- material frame
- blocking
- air
- aeration
- Prior art date
Links
- 238000005273 aeration Methods 0.000 title claims abstract description 63
- 238000006243 chemical reaction Methods 0.000 claims abstract description 108
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 38
- 239000002689 soil Substances 0.000 claims abstract description 21
- 230000004888 barrier function Effects 0.000 claims abstract description 6
- 239000000463 material Substances 0.000 claims description 109
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 abstract description 32
- 230000000694 effects Effects 0.000 abstract description 21
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 abstract description 16
- 229910052757 nitrogen Inorganic materials 0.000 abstract description 16
- 239000001301 oxygen Substances 0.000 abstract description 16
- 229910052760 oxygen Inorganic materials 0.000 abstract description 16
- 239000005416 organic matter Substances 0.000 abstract description 15
- 241000894006 Bacteria Species 0.000 abstract description 10
- 230000009286 beneficial effect Effects 0.000 abstract description 2
- 241000196324 Embryophyta Species 0.000 description 28
- 239000010865 sewage Substances 0.000 description 27
- 230000002708 enhancing effect Effects 0.000 description 19
- 239000003344 environmental pollutant Substances 0.000 description 10
- 231100000719 pollutant Toxicity 0.000 description 10
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 8
- 229910052698 phosphorus Inorganic materials 0.000 description 8
- 239000011574 phosphorus Substances 0.000 description 8
- 239000011362 coarse particle Substances 0.000 description 4
- 238000010586 diagram Methods 0.000 description 3
- 230000002550 fecal effect Effects 0.000 description 3
- 239000000945 filler Substances 0.000 description 3
- 239000010419 fine particle Substances 0.000 description 3
- 230000005764 inhibitory process Effects 0.000 description 3
- 238000000746 purification Methods 0.000 description 3
- 238000007789 sealing Methods 0.000 description 3
- 239000010802 sludge Substances 0.000 description 3
- 239000004912 1,5-cyclooctadiene Substances 0.000 description 2
- 101100233916 Saccharomyces cerevisiae (strain ATCC 204508 / S288c) KAR5 gene Proteins 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 238000000034 method Methods 0.000 description 2
- 244000005700 microbiome Species 0.000 description 2
- 239000000203 mixture Substances 0.000 description 2
- 238000012986 modification Methods 0.000 description 2
- 230000004048 modification Effects 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 235000005273 Canna coccinea Nutrition 0.000 description 1
- 240000008555 Canna flaccida Species 0.000 description 1
- 101001121408 Homo sapiens L-amino-acid oxidase Proteins 0.000 description 1
- 101000827703 Homo sapiens Polyphosphoinositide phosphatase Proteins 0.000 description 1
- 102100026388 L-amino-acid oxidase Human genes 0.000 description 1
- 244000273256 Phragmites communis Species 0.000 description 1
- 235000014676 Phragmites communis Nutrition 0.000 description 1
- 102100023591 Polyphosphoinositide phosphatase Human genes 0.000 description 1
- 101100012902 Saccharomyces cerevisiae (strain ATCC 204508 / S288c) FIG2 gene Proteins 0.000 description 1
- 229910000831 Steel Inorganic materials 0.000 description 1
- 240000001398 Typha domingensis Species 0.000 description 1
- 229910021536 Zeolite Inorganic materials 0.000 description 1
- 230000000903 blocking effect Effects 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 230000008094 contradictory effect Effects 0.000 description 1
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 description 1
- 239000007789 gas Substances 0.000 description 1
- 230000005484 gravity Effects 0.000 description 1
- 239000011159 matrix material Substances 0.000 description 1
- QJGQUHMNIGDVPM-UHFFFAOYSA-N nitrogen group Chemical group [N] QJGQUHMNIGDVPM-UHFFFAOYSA-N 0.000 description 1
- 238000006213 oxygenation reaction Methods 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 230000035699 permeability Effects 0.000 description 1
- 230000008635 plant growth Effects 0.000 description 1
- 230000008569 process Effects 0.000 description 1
- 239000011435 rock Substances 0.000 description 1
- 239000002893 slag Substances 0.000 description 1
- 239000010959 steel Substances 0.000 description 1
- 239000004575 stone Substances 0.000 description 1
- 238000006467 substitution reaction Methods 0.000 description 1
- 230000001360 synchronised effect Effects 0.000 description 1
- 230000002195 synergetic effect Effects 0.000 description 1
- 238000005406 washing Methods 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
- 239000010457 zeolite Substances 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/32—Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/30—Aerobic and anaerobic processes
- C02F3/302—Nitrification and denitrification treatment
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/34—Biological treatment of water, waste water, or sewage characterised by the microorganisms used
- C02F3/348—Biological treatment of water, waste water, or sewage characterised by the microorganisms used characterised by the way or the form in which the microorganisms are added or dosed
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F7/00—Aeration of stretches of water
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2201/00—Apparatus for treatment of water, waste water or sewage
- C02F2201/002—Construction details of the apparatus
- C02F2201/007—Modular design
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Definitions
- the invention relates to the technical field of artificial wetlands, in particular to a water-blocking, air-permeable, intermittently aerated modular artificial wetland.
- artificial wetlands mainly remove nitrogen-containing pollutants in sewage through nitrification and denitrification of microorganisms in the filler matrix.
- the nitrification reaction requires an aerobic environment, and the denitrification requires an anaerobic or anaerobic environment.
- the nitrification reaction the main nitrogen removal, is poor and the reaction rate is slow.
- Other aerobic and heterotrophic bacteria also produce other reactions to remove organic matter poorly, resulting in poor removal of organic matter and denitrification effects.
- the technical problem to be solved by the present invention is to provide a modular artificial wetland with clear aerobic and anoxic zones and water-blocking, air-permeable and intermittent aeration.
- a modular artificial wetland with water-blocking, breathable and intermittent aeration comprising an aerobic reaction zone, an anoxic reaction zone, a soil plant zone and an aeration pipe; the aerobic reaction zone, the anoxic reaction zone and the soil plant zone are connected in sequence along the water outlet direction from bottom to top, and the aerobic reaction zone comprises a breathable water-blocking layer and an air-isolating layer arranged at intervals from the inside to the outside, and the aeration port of the aeration pipe is located in the cavity enclosed by the breathable water-blocking layer and the air-isolating layer.
- the aerobic reaction zone also includes a first material frame spaced apart from the module frame and connected to the water inlet pipe, the aeration pipe passes through the module frame and the aeration port is located at the gap between the module frame and the first material frame, the air-permeable and water-blocking layer is arranged on the first material frame, and the air-isolating layer is arranged on the module.
- the anoxic reaction zone includes at least a second material frame
- the soil plant zone includes at least a third material frame.
- the second material frame and the third material frame can be detachably connected to the module frame in the vertical direction, and the second material frame can also be slidably and sealedly connected to the first material frame and the third material frame in the horizontal direction.
- the water inlet pipe is provided with at least four main water inlet openings, and the four main water inlet openings are evenly arranged around the module frame.
- the aeration pipe is provided with at least four main air inlet openings, and the four main air inlet openings are evenly arranged around the module frame.
- the second material frame is provided with a first flange and a second flange on the upper and lower sides respectively in the vertical direction, and the first flange can be slidably and sealedly connected with the second material frame in the horizontal direction, and the third material frame and the first material frame are provided with a first groove body and a second groove body which are sealingly plugged with the first flange and the second flange respectively, and the second groove body can be slidably and sealedly connected with the first material frame in the horizontal direction.
- both sides of the module frame are provided with limited sliding grooves in the vertical direction, a threaded rod is rotatably arranged in the limited sliding groove, two sliders are threadedly connected to the threaded rod, and the two sliders are slidably connected to the groove walls of the limited sliding groove respectively;
- the left and right sides of the second material frame are also respectively provided with first slide grooves in the horizontal direction, and first protrusions that can slide in the two limit slide grooves are respectively slidably arranged in the two first slide grooves, and the first protrusions can allow the threaded rod and the slider located above to pass through, and the first protrusions can also abut against the top of the slider located below;
- Second protrusions that can slide in the two limiting sliding grooves are also respectively arranged on both sides of the third material frame, and the second protrusions can allow the threaded rod to pass through and can abut against the top end of the sliding block located above.
- the first protrusion includes a block body, a sliding rod that slides through the block body in a vertical direction, two plug blocks that slide through the block body in a horizontal direction, a driving block that is arranged on the sliding rod and can control the two plug blocks to slide synchronously in the same direction, and a spring that is wound around the sliding rod and can reset the sliding rod, and the groove walls of the first sliding groove and the limiting sliding groove are respectively provided with slots that can be plugged in with the plug blocks, and the sliding rod can also abut against the second protrusion.
- the cross section of the driving block is a parallelogram
- one side of the two plug blocks is inclined and respectively contacts the two inclined surfaces of the driving block
- the two plug blocks are also slidably hinged to the driving block through connecting rods.
- a motor whose output end is connected to one of the threaded rods is also arranged in the module frame, and pulleys are arranged on both of the threaded rods, and a belt is connected between the two pulleys.
- the modular artificial wetland with water-blocking, air-permeable and intermittent aeration in the embodiment of the present invention is provided with an aerobic reaction zone, an anoxic reaction zone, a soil plant zone and an aeration pipe.
- the aerobic reaction zone includes an air-permeable water-blocking layer and an air-isolating layer arranged from inside to outside, and the aeration port of the aeration pipe is located in the cavity formed by the air-permeable water-blocking layer and the air-isolating layer:
- the concentration of nitrogen pollutants in sewage is reduced, avoiding the occurrence of wetland plant root rot caused by high concentrations of nitrogen pollutants in sewage, that is, enhancing the activity of plant roots. It can absorb and assimilate part of the phosphorus-containing pollutants, thus enhancing the phosphorus removal effect;
- nitrification reaction, denitrification reaction and plant purification are carried out in sequence and in an orderly manner, ensuring that each area can be completely covered by sewage for reaction, thereby improving the utilization rate of wetlands.
- FIG1 is a schematic diagram of the components of a water-blocking, air-permeable, intermittently aerated modular artificial wetland according to an embodiment of the present invention
- FIG2 is a front view of a modular artificial wetland structure with water-blocking, air-permeable and intermittent aeration according to an embodiment of the present invention
- FIG. 3 is a front cross-sectional view of a modular constructed wetland structure with water-blocking, air-permeable, intermittent aeration according to an embodiment of the present invention
- FIG4 is an enlarged view of portion A of FIG3 ;
- FIG5 is an enlarged cross-sectional view of portion B of FIG3 ;
- FIG. 6 is a front cross-sectional view of a modular constructed wetland structure with water-blocking, air-permeable, intermittent aeration according to an embodiment of the present invention
- FIG. 7 is a schematic diagram of the structure of a second material frame according to an embodiment of the present invention.
- FIG8 is a schematic diagram of the structure of a third material frame according to an embodiment of the present invention.
- FIG. 9 is a front view of a modular constructed wetland with water blocking, air permeability and intermittent aeration in a combined use state according to an embodiment of the present invention.
- FIG. 10 is a front view of the structure of another combined use state of the water-blocking, air-permeable, intermittently aerated modular artificial wetland according to an embodiment of the present invention.
- the embodiments of the present invention involve directional indications such as up, down, left, right, front, back, etc.
- the directional indications are only used to explain the relative position relationship, movement status, etc. between the components in a certain specific posture as shown in the accompanying drawings. If the specific posture changes, the directional indication will also change accordingly.
- the water-blocking, breathable, intermittently aerated modular artificial wetland of the present invention comprises an aerobic reaction zone 1, an anoxic reaction zone 2, a soil plant zone 3 and an aeration pipe 4; the aerobic reaction zone 1, the anoxic reaction zone 2 and the soil plant zone 3 are sequentially connected along the water outlet direction from bottom to top, and the aerobic reaction zone 1 comprises a breathable water-blocking layer 5 and an air-isolating layer 6 arranged at intervals from inside to outside, and the aeration port of the aeration pipe 4 is located in the cavity enclosed by the breathable water-blocking layer 5 and the air-isolating layer 6.
- the modular artificial wetland with water-blocking, air-permeable and intermittent aeration in the embodiment of the present invention is provided with an aerobic reaction zone 1, an anoxic reaction zone 2, a soil plant zone 3 and an aeration pipe 4.
- the aerobic reaction zone 1 includes an air-permeable water-blocking layer 5 and an air-isolating layer 6 arranged from inside to outside, and the aeration port of the aeration pipe 4 is located in the cavity formed by the air-permeable water-blocking layer 5 and the air-isolating layer 6:
- Aeration and oxygenation are supplied to the aerobic reaction zone 1 through the aeration pipe 4, so that the dissolved oxygen in the aerobic reaction zone 1 is sufficient, forming a clear aerobic reaction zone for nitrification reaction and other denitrification reactions of aerobic and heterotrophic bacteria.
- the reaction of removing organic matter and enhancing the nitrification reaction effect provide sufficient nitrogen source for the denitrification reaction to occur, and by controlling the intermittent aeration of the aeration pipe 4 and controlling the aeration time, excessive oxygen is prevented from entering the anoxic reaction zone 2, forming a clear anoxic reaction zone 2, avoiding the inhibition of the denitrification reaction due to excessive dissolved oxygen while enhancing the denitrification reaction, thereby enhancing the nitrogen removal effect;
- the oxygen generated by the aeration tube 4 sandwiched between the two layers is locked, and the sewage in the aerobic reaction zone is locked, thereby further enhancing the nitrification reaction of the sewage in the aerobic reaction zone 1 and other organic matter removal reactions;
- nitrification reaction, denitrification reaction and plant purification are carried out in sequence and in an orderly manner, ensuring that each area can be completely covered by sewage for reaction, thereby improving the utilization rate of wetlands.
- the aerobic reaction zone 1, the anoxic reaction zone 2 and the soil plant zone 3 are all in a grid-like structure at the bottom and open at the top, and the aeration cycle is aeration for 5 hours and aeration for 1 hour, with four cycles per day.
- Table 1 Composition of rural fecal sewage
- the device of the present invention was used for treatment, and an ordinary artificial wetland without aeration and a top-down sewage treatment artificial wetland was used as a comparison.
- the artificial wetland was operated for 30 days, and the COD, nitrogen, phosphorus and other indicators were measured (as shown in Table 4).
- the aerobic reaction zone 1 includes a first material frame 101 spaced apart from the module frame 7 and connected to the water inlet pipe 8.
- the aeration pipe 4 is inserted through the module frame 7 and the aeration port is located at the gap between the module frame 7 and the first material frame 101.
- the air-permeable and water-blocking layer 5 is arranged on the first material frame 101, and the air-isolating layer 6 is arranged on the module frame 7.
- the air barrier layer 6 is arranged on the inner wall of the module frame 7 and the position where the corresponding aeration pipe 4 and the water inlet pipe 8 of the module frame 7 are penetrated, the air-permeable and water-blocking layer 5 can be arranged on the inner and outer walls of the first material frame 101, and the air-permeable and water-blocking layer 5 can adopt an air-permeable and water-blocking film, and the air barrier layer 6 adopts an air-blocking film to ensure that the gas in the aeration pipe 4 is completely in the gap position between the first material frame 101 and the module frame 7 and in the first material frame 101, and the aeration pipe 4 aerates the three sides of the bottom of the first material frame 101, and the water inlet pipe 8 inlets water to the two sides of the bottom of the first material frame 101;
- the aerobic reaction zone 1 also includes coarse particles arranged in the first material frame 101, and the diameter of the coarse particles ranges from 5 cm to 10 cm.
- the types of coarse particles can be selected from the group particles used in existing artificial wetlands, including crushed stone, gravel, and volcanic rock, which have certain mechanical strength, large specific surface area, suitable porosity, and good biological and chemical stability, and can be mixed or single-type filled when filling.
- the anoxic reaction zone 2 comprises at least a second material frame 201
- the soil plant zone 3 at least includes a third material frame 301
- the second material frame 201 and the third material frame 301 can be detachably connected to the module frame 7 in the vertical direction
- the second material frame 201 can also be slidably and sealedly connected to the first material frame 101 and the third material frame 301 in the horizontal direction.
- This design realizes the modularization of the wetland, which is detachable and easy to install and has mobility; when the wetland is blocked, the second material frame 201 can be slid horizontally to expose the second material frame 201 and the first material frame 101 to the outside, so that the filling inside them can be easily cleaned, and the filling inside the third material frame 301 can be cleaned directly from the top;
- the anoxic reaction zone 2 also includes fine particles arranged in the second material frame 201, and the diameter of the fine particles ranges from 1 cm to 5 cm.
- the specific types of coarse particles can be selected from the fine particles used in existing artificial wetlands, including ceramsite, zeolite, and steel slag, which have certain mechanical strength and suitable porosity, and can be mixed or single-type filled when specifically filled;
- the soil and plant area 3 also includes soil and plants arranged in the third material frame 301.
- the soil and the specific types of the soil and plants are the soil and plants used in existing artificial wetlands.
- the specific plants can be selected from aquatic plants with well-developed root systems and strong vitality, such as reeds, cannas, cattails, etc.
- the water inlet pipe 8 is provided with at least four main water inlet openings 801, and the four main water inlet openings 801 are evenly arranged around the module frame 7.
- the present invention can be used alone, or multiple main water inlet openings 801 can be spliced and combined for use.
- the aeration pipe 4 is provided with at least four main air inlet openings 401, and the four main air inlet openings 401 are evenly arranged around the module frame 7.
- the present invention can be used individually, or multiple main air inlet openings 401 can be spliced and combined for use.
- the water outlet pipe assembly 14 also includes a water outlet pipe assembly 14 connected to the third material frame 301, and the water outlet pipe assembly 14 includes a bellows 1401 detachably connected to the third material frame 301 and a fixing member disposed on the bellows 1401 for rotating and fixing the water outlet direction of the bellows 1401.
- the water outlet direction of the bellows 1401 is adjusted by rotating the fixing member, so that the water outlet level of the bellows 1401 is adjustable, and the water outlet at a lower water level can be adjusted in the early stage of wetland use to facilitate the growth of plant roots.
- the fixing member includes a support frame 1405 disposed on the third material frame 301, a fixing ring 1402 rotatably disposed on the support frame 1405, and at least two threads connected to the fixing ring.
- the bolt 1404 on the support frame 1402 and the clamping block 1403 rotatably connected to the bolt 1404, and the clamping surface of the clamping block 1403 is in a corrugated shape matching the bellows 1401. This design makes the bellows 1401 have a good fixing effect and is convenient for adjusting the angle.
- the rotation connection between the fixing ring 1402 and the support frame 1405 is a rotation connection method that can be fixed after rotation in the prior art, which will not be described in detail here.
- the bellows 1401 can be detachably connected to the main water inlet 801. With this design, sewage can be repeatedly treated after being spliced in the wetland, thereby enhancing the treatment effect.
- the upper and lower sides of the second material frame 201 are respectively provided with a first flange 202 and a second flange 203 in the vertical direction, and the first flange 202 can be slidably and sealedly connected with the second material frame 201 in the horizontal direction, and the third material frame 301 and the first material frame 101 are respectively provided with a first groove body 302 and a second groove body 102 which are sealed and plugged with the first flange 202 and the second flange 203, and the second groove body 102 can be slidably and sealedly connected with the first material frame 101 in the horizontal direction.
- the sealing connection between the material frames is realized by plug-in matching, the sealing effect is good, the structure is simple, and the manufacturing cost is low.
- both sides of the module frame 7 are provided with limited sliding grooves 701 in the vertical direction, and a threaded rod 9 is rotatably arranged in the limited sliding groove 701.
- Two sliders 10 are threadedly connected to the threaded rod 9, and the two sliders 10 are slidably connected to the groove walls of the limited sliding groove 701 respectively.
- the left and right sides of the second material frame 201 are respectively provided with first slide grooves 2011 in the horizontal direction, and first protrusions 204 that can slide in the two limiting slide grooves 701 are respectively slidably arranged in the two first slide grooves 2011, and the first protrusions 204 can allow the threaded rod 9 and the slider 10 located above to pass through, and the first protrusions 204 can also abut against the top of the slider 10 located below;
- the two sides of the third material frame 301 are also provided with second protrusions 303 that can slide in the two limiting slide grooves 701, and the second protrusions 303 can allow the threaded rod 9 to pass through and can abut against the top of the slider 10 located above.
- This design avoids the situation that when the wetland is blocked, the second material frame 201 is difficult to slide in the horizontal direction due to the large friction between the second material frame 201 and the third material frame 301 and the first material frame 101. In the specific use state, by rotating the threaded rod 9, the threaded rod 9 and the slider 10 are realized.
- the screw-nut combination enables the slider 10 to move in the vertical direction, and the two sliders 10 lift the second material frame 201 and the third material frame 301 respectively, so that there is a gap between the second material frame 201 and the first material frame 101 and the third material frame 301, so that it is convenient to pull the second material frame 201 and the fillers in the second material frame 201 and the first material frame 101 are convenient to clean; and in this embodiment, the sliding between the limiting slide groove 701 and the first protrusion 204 and the second protrusion 303 is convenient for plugging and matching the first flange 202 and the second flange 203 with the first groove body 302 and the second groove body 102; and in this embodiment, the threaded rod 9 can be set in only one limiting slide groove 701.
- the first protrusion 204 includes a block body 2041, a sliding rod 2042 that slides through the block body 2041 in a vertical direction, two plug blocks 2043 that slide through the block body 2041 in a horizontal direction, a driving block 2044 that is arranged on the sliding rod 2042 and can control the two plug blocks 2043 to slide synchronously in the same direction, and a spring 2045 that is wound around the sliding rod 2042 and can reset the sliding rod 2042, and the first sliding groove 2011 and the groove wall of the limiting sliding groove 701 are respectively provided with slots 7011 that can be plugged into and cooperate with the plug blocks 2043, and the sliding rod 2042 can also be against the second protrusion 303.
- This design allows the first protrusion 204 to be fixed on the second material frame 201 when the second material frame 201 is not installed on the module frame 7, so that the first protrusion 204 is installed in the same position as the limiting slide groove 701. After the second material frame 201 is not installed on the module frame 7, the first protrusion 204 is fixed on the module frame 7, so that the second material frame 201 can slide in the horizontal direction. In a specific state, when the first protrusion 204 is fixed on the second material frame 201, an insert block 2043 is inserted into the slot 7011 of the second material frame 201.
- the slide bar 2042 After the first protrusion 204 is fixed on the module frame 7, as the third material frame 301 is installed, the slide bar 2042 abuts against the second protrusion 303, driving the slide bar 2042 to slide, thereby driving the insert into the slot 7011 of the second material frame 201.
- the insert block 2043 in the slot 7011 on the module frame 7 is detached, and the other insert block 2043 is inserted into the slot 7011 on the module frame 7.
- the sliding rod 2042 After the third material frame 301 is installed and disassembled, the sliding rod 2042 is reset by the spring 2045, and the insert block 2043 detached from the slot 7011 of the second material frame 201 is reinserted.
- the cross section of the driving block 2044 is a parallelogram
- one side of the two plug blocks 2043 is inclined and respectively contacts the two inclined surfaces of the driving block 2044
- the two plug blocks 2043 are also respectively slidably hinged with the driving block 2044 through the connecting rod 2046.
- a synchronous sliding effect is achieved through the design of simple inclined surfaces and connecting rods 2046, and the structure is ingenious and simple to manufacture.
- the threads of the threaded rod 9 are distributed in two sections, and the pitch of the thread located at the upper part is greater than the pitch of the thread located at the lower part.
- a motor 11 whose output end is connected to one of the threaded rods 9 is further provided in the module frame 7, and pulleys 12 are further provided on the two threaded rods 9, and a belt 13 is further connected between the two pulleys 12.
- the two threaded rods 9 are synchronously rotated, so that the third material frame 301 and the second material frame 201 can be stably raised and lowered.
- the water-blocking, air-permeable, intermittently aerated modular artificial wetland of the present invention is:
- the aeration pipe 4 is used to aerate and supply oxygen to the aerobic reaction zone 1, so that the dissolved oxygen in the aerobic reaction zone 1 is sufficient, forming a clear aerobic reaction zone for nitrification reaction and other organic matter removal reactions of other aerobic heterotrophic bacteria, and by enhancing the nitrification reaction effect, sufficient nitrogen source is provided for the denitrification reaction to cause the denitrification reaction, and the controllable intermittent aeration pipe 4 can control the aeration time to prevent excessive oxygen from entering the anoxic reaction zone 2, forming a clear anoxic reaction zone 2, avoiding the inhibition of the denitrification reaction due to excessive dissolved oxygen while enhancing the denitrification reaction, thereby enhancing the nitrogen removal effect;
- the oxygen generated by the aeration tube 4 sandwiched between the two layers is locked, and the sewage in the aerobic reaction zone is locked, thereby further enhancing the nitrification reaction of the sewage in the aerobic reaction zone 1 and other organic matter removal reactions;
- the first material frame 101, the second material frame 201, the third material frame 301 are detachably connected to the module frame 7, so that the wetland device can be detachably installed and is easy to install;
- the second material frame 201 and the third material frame 301 are exposed to the outside by sliding the second material frame 201 in the horizontal direction, so as to facilitate cleaning of the fillers inside.
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- Life Sciences & Earth Sciences (AREA)
- Engineering & Computer Science (AREA)
- Organic Chemistry (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Chemical & Material Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Microbiology (AREA)
- Biodiversity & Conservation Biology (AREA)
- Biotechnology (AREA)
- Botany (AREA)
- Treatment Of Biological Wastes In General (AREA)
- Biological Treatment Of Waste Water (AREA)
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
Abstract
本发明公开了一种阻水透气间歇曝气的模块式人工湿地,包括好氧反应区、缺氧反应区、土壤植物区以及曝气管;所述好氧反应区、所述缺氧反应区以及所述土壤植物区沿自下而上的出水方向依次连通,且所述好氧反应区包括由内至外间隔设置的透气阻水层和隔气层,所述曝气管的曝气口位于所述透气阻水层以及所述隔气层围合的空腔内。本发明有助于解决现有大部分湿地很难形成溶解氧较高的好氧区,且湿地内存在其他好氧异氧菌会发生其他去除有机物的反应,使得主要除氮的硝化反应不佳,反应速率慢,其他好氧异氧菌发生其他去除有机物的反应也不佳,造成了去除有机物和脱氮效果均不佳的问题。
Description
本发明涉及人工湿地技术领域,具体地说涉及一种阻水透气间歇曝气的模块式人工湿地。
人工湿地是20世纪70年代兴起的一种新型污水处理技术,将污水、污泥有控制的投配到经人工建造的湿地上,污水与污泥在沿一定方向流动的过程中,主要利用土壤、人工介质、植物、微生物的物理、化学、生物三重协同作用,对污水、污泥进行处理的一种技术,被广泛应用于小城镇和农村地区的污水处理中。
目前人工湿地主要通过填料基质中微生物的硝化和反硝化作用来实现污水中的含氮污染物的去除,且其中硝化反应需要有氧环境,反硝化需要通过缺氧或无氧环境,但是由于现有大部分湿地很难形成溶解氧较高的好氧区,且湿地内存在其他好氧异氧菌会发生其他去除有机物的反应,使得主要除氮的硝化反应不佳,反应速率慢,其他好氧异氧菌发生其他去除有机物的反应也不佳,造成了去除有机物和脱氮效果均不佳。
发明内容
本发明所要解决的技术问题是提供一种好氧、缺氧明确分区的阻水透气间歇曝气的模块式人工湿地。
为了解决上述技术问题,本发明采用如下技术方案:一种阻水透气间歇曝气的模块式人工湿地,包括好氧反应区、缺氧反应区、土壤植物区以及曝气管;所述好氧反应区、所述缺氧反应区以及所述土壤植物区沿自下而上的出水方向依次连通,且所述好氧反应区包括由内至外间隔设置的透气阻水层和隔气层,所述曝气管的曝气口位于所述透气阻水层以及所述隔气层围合的空腔内。
进一步的,还包括模块架以及穿设在所述模块架上的进水管,所述好氧反应区还包括与所述模块架间隔设置且与所述进水管相连通的第一料框,所述曝气管穿设在所述模块架上且曝气口位于所述模块架与所述第一料框的间隙位置处,所述透气阻水层设置在所述第一料框上,所述隔气层设置在所述模块上。
进一步的,所述缺氧反应区至少包括第二料框,所述土壤植物区至少包括第三料框,所述第二料框以及所述第三料框均可沿竖直方向与所述模块架可拆卸式连接,且所述第二料框还可沿水平方向与所述第一料框以及所述第三料框滑动密封连接。
进一步的,所述进水管设置有至少四个主进水管口,且四个所述主进水管口均匀的穿设在模块架的四周。
进一步的,所述曝气管设置有至少四个主进气管口,且四个所述主进气管口均匀的穿设在模块架的四周。
进一步的,所述第二料框的上下两侧分别沿竖直方向设置有第一凸缘和第二凸缘,且所述第一凸缘可沿水平方向与所述第二料框滑动密封连接,所述第三料框以及所述第一料框上分别设置有与所述第一凸缘以及所述第二凸缘密封插接配合的第一凹槽体和第二凹槽体,且所述第二凹槽体可沿水平方向与所述第一料框滑动密封连接。
进一步的,所述模块架的两侧还分别沿竖直方向开设有限位滑槽,所述限位滑槽内还转动设置有螺纹杆,所述螺纹杆上还螺纹连接有两个滑块,且两个所述滑块还分别与所述限位滑槽的槽壁滑动连接;
所述第二料框的左右两侧还分别沿水平方向开设有第一滑槽,两个所述第一滑槽内分别滑动设置有可在两个所述限位滑槽内滑动的第一凸块,且所述第一凸块可供所述螺纹杆以及位于上方的所述滑块穿过,且所述第一凸块还可抵在位于下方的所述滑块的顶端;
所述第三料框的两侧还分别设置有可在两个所述限位滑槽内滑动第二凸块,且所述第二凸块可供所述螺纹杆穿过且可抵在位于上方的所述滑块的顶端。
进一步的,所述第一凸块包括块体、沿竖直方向滑动穿设在所述块体上的滑竿、两个分别沿水平方向滑动穿设在所述块体上的插块、设置在所述滑竿上且可控制两个所述插块沿同一方向同步滑动的驱动块以及绕设在所述滑竿上可将所述滑竿复位的弹簧,且所述第一滑槽以及所述限位滑槽的槽壁上还分别开设有可与所述插块插接配合的插槽,且所述滑竿还可与所述第二凸块相抵。
进一步的,所述驱动块的截面呈平行四边形,两个所述插块的一侧分别呈倾斜状且分别与所述驱动块的两个倾斜面相接触,且两个插块还分别与所述驱动块通过连杆滑动铰接。
进一步的,所述模块架内还设置有输出端与一个所述螺纹杆相连接的电机,且两个所述螺纹杆上均还设置有皮带轮,两个所述皮带轮间还连接有皮带。
本发明的有益效果体现在:
本发明实施例阻水透气间歇曝气的模块式人工湿地设置有好氧反应区、缺氧反应区、土壤植物区以及曝气管,好氧反应区包括由内至外间隔设置的透气阻水层和隔气层,曝气管的曝气口位于透气阻水层和隔气层形成的空腔内:
1.通过曝气管向好氧反应区曝气供氧,使得好氧反应区内的溶解氧充足,形成明确的好氧反应区发生硝化反应以及发生其他好氧异氧菌的其他去除有机物的反应,且通过增强硝化反应效果,为反硝化反应提供了充足的氮源发生反硝化反应,且通过控制曝气管间歇式曝气以及控制曝气时间,防止氧气过量导致氧气进入缺氧反应区,形成明确的缺氧反应区,避免由于溶解氧过量抑制反硝化反应的同时又增强了反硝化反应,以此增强了除氮效果;
2.通过设置透气阻水层以及隔气层,将夹持在两层之间由曝气管产生氧气锁住以及将好氧反应区内的污水锁住,进一步增强了污水在好氧反应区内的硝化反应以及其他有机物去除反应;
3.通过增强硝化反应、其他好氧异氧菌的其他去除有机物的反应以及反硝化反应,降低了污水内含氮污染物的浓度,避免了污水内含氮污染物浓度较高导致湿地植物根系腐烂的情况发生,即增强了植物根系的活性,由于植物根系
可将一部分含磷污染物吸收和同化,故也增强了除磷效果;
4.通过设置自下而上出水,实现硝化反应、反硝化反应以及植物净化依次有序进行,确保每个区间可完全被污水覆盖进行反应,提高湿地利用率。
图1是本发明实施例阻水透气间歇曝气的模块式人工湿地组成成分示意图;
图2是本发明实施例阻水透气间歇曝气的模块式人工湿地结构正视图;
图3是本发明实施例阻水透气间歇曝气的模块式人工湿地结构正视剖视图;
图4是图3的A部放大图;
图5是图3的B部放大剖视图;
图6是本发明实施例阻水透气间歇曝气的模块式人工湿地结构正视剖视图;
图7是本发明实施例第二料框结构示意图;
图8是本发明实施例第三料框结构示意图;
图9是本发明实施例阻水透气间歇曝气的模块式人工湿地一组合使用状态结构正视图;
图10是本发明实施例阻水透气间歇曝气的模块式人工湿地另一组合使用状态结构正视图。
附图中各部件的标记为:1、好氧反应区;101、第一料框;102、第二凹槽体;2、缺氧反应区;201、第二料框;2011、第一滑槽;202、第一凸缘;203、第二凸缘;204、第一凸块;2041、块体;2042、滑竿;2043、插块;2044、驱动块;2045、弹簧;2046、连杆;3、土壤植物区;301、第三料框;302、第一凹槽体;303、第二凸块;4、曝气管;401、主进气管口;5、透气阻水层;6、隔气层;7、模块架;701、限位滑槽;7011、插槽;8、进水管;801、主进水管口;9、螺纹杆;10、滑块;11、电机;12、皮带轮;13、皮带;14、出水管;1401、波纹管;1402、固定环;1403、夹块;1404、螺栓;1405、支撑架。
下面将结合本发明实施例中的附图,对本发明实施例中的技术方案进行清楚、完整地描述,显然,所描述的实施例仅仅是本发明的一部分实施例,而不是全部的实施例。
需要说明,若本发明实施例中有涉及方向性指示诸如上、下、左、右、前、后……,则该方向性指示仅用于解释在某一特定姿态如附图所示下各部件之间的相对位置关系、运动情况等,如果该特定姿态发生改变时,则该方向性指示也相应地随之改变。
另外,若本发明实施例中有涉及“第一”、“第二”等的描述,则该“第一”、“第二”等的描述仅用于描述目的,而不能理解为指示或暗示其相对重要性或者隐含指明所指示的技术特征的数量。由此,限定有“第一”、“第二”的特征可以明示或者隐含地包括至少一个该特征。另外,“多个”指两个以上。另外,各个实施例之间的技术方案可以相互结合,但是必须是以本领域普通技术人员能够实现为基础,当技术方案的结合出现相互矛盾或无法实现时应当认为这种技术方案的结合不存在,也不在本发明要求的保护范围之内。
参见图1至图10。
本发明阻水透气间歇曝气的模块式人工湿地,包括好氧反应区1、缺氧反应区2、土壤植物区3以及曝气管4;所述好氧反应区1、所述缺氧反应区2以及所述土壤植物区3沿自下而上的出水方向依次连通,且所述好氧反应区1包括由内至外间隔设置的透气阻水层5和隔气层6,所述曝气管4的曝气口位于所述透气阻水层5以及所述隔气层6围合的空腔内。
本发明实施例阻水透气间歇曝气的模块式人工湿地设置有好氧反应区1、缺氧反应区2、土壤植物区3以及曝气管4,好氧反应区1包括由内至外间隔设置的透气阻水层5和隔气层6,曝气管4的曝气口位于透气阻水层5和隔气层6形成的空腔内:
1.通过曝气管4向好氧反应区1曝气供氧,使得好氧反应区1内的溶解氧充足,形成明确的好氧反应区发生硝化反应以及发生其他好氧异氧菌的其他去
除有机物的反应,且通过增强硝化反应效果,为反硝化反应提供了充足的氮源发生反硝化反应,且通过控制曝气管4间歇式曝气以及控制曝气时间,防止氧气过量导致氧气进入缺氧反应区2,形成明确的缺氧反应区2,避免由于溶解氧过量抑制反硝化反应的同时又增强了反硝化反应,以此增强了除氮效果;
2.通过设置透气阻水层5以及隔气层6,将夹持在两层之间由曝气管4产生氧气锁住以及将好氧反应区内的污水锁住,进一步增强了污水在好氧反应区1内的硝化反应以及其他有机物去除反应;
3.通过增强硝化反应、其他好氧异氧菌的其他去除有机物的反应以及反硝化反应降低了污水内含氮污染物的浓度,避免了污水内含氮污染物浓度较高导致湿地植物根系腐烂的情况发生,即增强了植物根系的活性,由于植物根系可将一部分含磷污染物吸收和同化,故也增强了除磷效果;
4.通过设置自下而上出水,实现硝化反应、反硝化反应以及植物净化依次有序进行,确保每个区间可完全被污水覆盖进行反应,提高湿地利用率。
且在本发明中,好氧反应区1、缺氧反应区2和土壤植物区3均为底部网格状,顶部敞开的结构,曝气周期为曝气5h停止曝气1h,一天四个周期。
且在本实施例中:1.通过配制农村粪便污水(如表1所示),利用本发明装置进行处理,利用普通的人工湿地,不曝气,自上而下污水处理的人工湿地作为对比,运行30天,测定COD氮磷等指标(如表2所示)。
表1农村粪便污水成分表
表2不同操作效果对比
2.通过配制农村洗涤、洗漱等废水(如表3所示),利用本发明装置进行处理,利用普通的人工湿地,不曝气,自上而下污水处理的人工湿地作为对比,运行30天,测定COD氮磷等指标(如表4所示)。
表3农村粪便污水成分表
表4不同操作效果对比
在一实施例中,还包括模块架7以及穿设在所述模块架7上的进水管8,所述好氧反应区1海包括与所述模块架7间隔设置且与所述进水管8相连通的第一料框101,所述曝气管4穿设在所述模块架7上且曝气口位于所述模块架7与所述第一料框101的间隙位置处,所述透气阻水层5设置在所述第一料框101上,所述隔气层6设置在所述模块架7上。在本实施例中,隔气层6设置在模块架7的内壁以及模块架7相应曝气管4以及进水管8穿设的位置处,透气阻水层5设置在第一料框101的内外壁均可,且透气阻水层5可采用透气阻水膜,隔气层6采用阻气膜,确保曝气管4的气体完全处于第一料框101内与所述模块架7的间隙位置处以及第一料框101内,且曝气管4对第一料框101的底部三侧进行曝气,进水管8对第一料框101的底部两侧进行进水;
且在该实施例中,好氧反应区1还包括设置在第一料框101内的粗颗粒,且粗颗粒直径范围为5cm-10cm。且在本实施例中,粗颗粒的种类可选用现有人工湿地中所使用的组颗粒包括碎石、砾石、火山岩,具有一定机械强度、比表面积大并具有合适的孔隙率以及良好的生物和化学稳定性,且在具体填充时可进行混合种类填充或单种类填充。
在一实施例中,所述缺氧反应区2至少包括第二料框201,所述土壤植物区
3至少包括第三料框301,所述第二料框201以及所述第三料框301均可沿竖直方向与所述模块架7可拆卸式连接,且所述第二料框201还可沿水平方向与所述第一料框101以及所述第三料框301滑动密封连接。这样设计,实现湿地模块化,可拆卸安装、便于安装且具有可移动性;实现湿地堵塞时,通过沿水平方向滑动第二料框201,即可将第二料框201以及第一料框101暴露在外,方便对其内部的填料进行清洁,第三料框301内的填料直接从其顶部即可实现清洁;
且在该实施例中,缺氧反应区2还包括设置在第二料框201内的细颗粒,且细颗粒的直径范围为1cm-5cm,粗颗粒的具体种类可选用现有人工湿地中所使用的细颗粒包括陶粒、沸石、钢渣,具有一定机械强度且具有合适的孔隙率,且在具体填充时可进行混合种类填充或单种类填充;
且在该实施例中,土壤植物区3还包括设置在第三料框301内的土壤以及植株,土壤且土壤以及植株具体种类为现有人工湿地中所使用的土壤以及植株,具体植株可选用例如芦苇、美人蕉、香蒲等根系发达且生命力较强的水生植物。
在一实施例中,所述进水管8设置有至少四个主进水管口801,且四个所述主进水管口801均匀的穿设在模块架7的四周。这样设计,实现本发明可单个使用,也可将多个通过主进水管口801相互拼接组合使用。
在一实施例中,所述曝气管4设置有至少四个主进气管口401,且四个所述主进气管口401均匀的穿设在模块架7的四周。这样设计,实现本发明可单个使用,也可将多个通过主进气管口401相互拼接组合使用。
在一实施例中,还包括连通在所述第三料框301上的出水管组件14,所述出水管组件14包括可拆卸的连接在所述第三料框301上的波纹管1401以及设置在所述波纹管1401上的用于转动以及固定所述波纹管1401出水方向的固定件。这样设计,通过转动固定件调节波纹管1401的出水方向,实现波纹管1401的出水水位可调,在湿地使用初期可调节较低水位出水便于植物的根系生长。
在一实施例中,所述固定件包括设置在所述第三料框301上的支撑架1405、转动设置在所述支撑架1405上的固定环1402、至少两个螺纹连接在所述固定环
1402上的螺栓1404以及转动连接在所述螺栓1404上的夹块1403,且所述夹块1403的夹持面呈与所述波纹管1401匹配的波纹状。这样设计,使得波纹管1401的固定效果好以及便于调节角度,且在本实施例中,设置固定环1402与支撑架1405的转动连接为现有技术中转动后可固定的转动连接方式,在此不做过多赘述。
在一实施例中,所述波纹管1401可与所述主进水管口801可拆卸式连通。这样设计,在湿地拼接后可实现污水多次重复处理,增强处理效果。
在一实施例中,所述第二料框201的上下两侧分别沿竖直方向设置有第一凸缘202和第二凸缘203,且所述第一凸缘202可沿水平方向与所述第二料框201滑动密封连接,所述第三料框301以及所述第一料框101上分别设置有与所述第一凸缘202以及所述第二凸缘203密封插接配合的第一凹槽体302和第二凹槽体102,且所述第二凹槽体102可沿水平方向与所述第一料框101滑动密封连接。这样设计,通过插接配合实现各料框间的密封连接,密封效果好且结构简单、制作成本低。
在一实施例中,所述模块架7的两侧还分别沿竖直方向开设有限位滑槽701,所述限位滑槽701内还转动设置有螺纹杆9,所述螺纹杆9上还螺纹连接有两个滑块10,且两个所述滑块10还分别与所述限位滑槽701的槽壁滑动连接;
所述第二料框201的左右两侧还分别沿水平方向开设有第一滑槽2011,两个所述第一滑槽2011内分别滑动设置有可在两个所述限位滑槽701内滑动的第一凸块204,且所述第一凸块204可供所述螺纹杆9以及位于上方的所述滑块10穿过,且所述第一凸块204还可抵在位于下方的所述滑块10的顶端;
所述第三料框301的两侧还分别设置有可在两个所述限位滑槽701内滑动第二凸块303,且所述第二凸块303可供所述螺纹杆9穿过且可抵在位于上方的所述滑块10的顶端。这样设计,避免在湿地堵塞时,出现由于第二料框201与第三料框301以及第一料框101间的摩擦力较大,第二料框201难以沿水平方向滑动的情况,具体使用状态时,通过转动螺纹杆9,螺纹杆9与滑块10实现
丝杆螺母组合,使得滑块10沿竖直方向运动,两个滑块10分别将第二料框201以及第三料框301抬起,让第二料框201与第一料框101以及第三料框301间存在空隙即可,此时便于拉动第二料框201,便于对第二料框201以及第一料框101内填料进行清洗;且在本实施例中,设置的限位滑槽701与第一凸块204以及第二凸块303间的滑动是便于将第一凸缘202与第二凸缘203与第一凹槽体302和第二凹槽体102插接配合;且在本实施例中,可仅在一个限位滑槽701内设置螺纹杆9。
在一实施例中,所述第一凸块204包括块体2041、沿竖直方向滑动穿设在所述块体2041上的滑竿2042、两个分别沿水平方向滑动穿设在所述块体2041上的插块2043、设置在所述滑竿2042上且可控制两个所述插块2043沿同一方向同步滑动的驱动块2044以及绕设在所述滑竿2042上可将所述滑竿2042复位的弹簧2045,且所述第一滑槽2011以及所述限位滑槽701的槽壁上还分别开设有可与所述插块2043插接配合的插槽7011,且所述滑竿2042还可与所述第二凸块303相抵。这样设计,使得第一凸块204在第二料框201未安装于模块架7上时,第一凸块204是固定在第二料框201上的,便于第一凸块204与限位滑槽701的对位安装,第二料框201未安装于模块架7上后,第一凸块204固定于模块架7上,便于第二料框201实现沿水平方向滑动,且具体状态下,第一凸块204固定在第二料框201上时,一个插块2043插设在第二料框201的插槽7011内,第一凸块204固定于模块架7上后,随第三料框301的安装,滑竿2042与所述第二凸块303相抵,驱动滑竿2042滑动,带动插入第二料框201的插槽7011内的插块2043脱离,另一插块2043插入模块架7上的插槽7011内,第三料框301的安装拆卸后,滑竿2042通过弹簧2045复位,将脱离第二料框201的插槽7011内的插块2043重新插入,且在本实施例中,在通过螺纹杆9实现第二料框201以及第三料框301移动时,第二凸块303还是抵在第一凸块204上的,并实现插块2043模块架7上的插槽7011内,为确保此效果,可在第二凸块303底部穿设一压块,压块通过另一弹簧与第二凸块303连接,且该弹簧的弹性系数要大于弹簧2045的弹性系数,且该弹簧不影响第二凸缘203与第一
凹槽体302的密封插接。
在一实施例中,所述驱动块2044的截面呈平行四边形,两个所述插块2043的一侧分别呈倾斜状且分别与所述驱动块2044的两个倾斜面相接触,且两个插块2043还分别与所述驱动块2044通过连杆2046滑动铰接。这样设计,通过简单倾斜面以及连杆2046的设计实现同步滑动效果,结构巧妙且制作简单。
在一实施例中,所述螺纹杆9的螺纹呈两段分布,且位于上方的螺纹螺距大于位于下方的螺纹螺距。这样设计,使得螺纹杆9转动时,第三料框301上移的距离大,避免由于重力,第三料框301结构下沉贴于第二料框201,使得第二料框201也下沉,使得需要转动螺纹杆9圈数较多才能实现第二料框201沿水平方向的自由滑动。
在一实施例中,所述模块架7内还设置有输出端与一个所述螺纹杆9相连接的电机11,且两个所述螺纹杆9上均还设置有皮带轮12,两个所述皮带轮12间还连接有皮带13。这样设计,通过电机11、皮带轮12以及皮带13的配合,实现两个螺纹杆9同步转动,使得第三料框301以及第二料框201上升以及下降稳定。
综上所述,本发明阻水透气间歇曝气的模块式人工湿地:
1.通过曝气管4向好氧反应区1曝气供氧,使得好氧反应区1内的溶解氧充足,形成明确的好氧反应区发生硝化反应以及发生其他好氧异氧菌的其他去除有机物的反应,且通过增强硝化反应效果,为反硝化反应提供了充足的氮源发生反硝化反应,且通过可控制间歇式曝气管4,可控制曝气时间,防止氧气过量导致氧气进入缺氧反应区2,形成明确的缺氧反应区2,避免由于溶解氧过量抑制反硝化反应的同时又增强了反硝化反应,以此增强了除氮效果;
2.通过设置透气阻水层5以及隔气层6,将夹持在两层之间由曝气管4产生氧气锁住以及将好氧反应区内的污水锁住,进一步增强了污水在好氧反应区1内的硝化反应以及其他有机物去除反应;
3.通过增强硝化反应、其他好氧异氧菌的其他去除有机物的反应以及反硝
化反应降低了污水内含氮污染物的浓度,避免了污水内含氮污染物浓度较高导致湿地植物根系腐烂的情况发生,即增强了植物根系的活性,由于植物根系可将一部分含磷污染物吸收和同化,故也增强了除磷效果;
4.通过设置自下而上出水,实现硝化反应、反硝化反应以及植物净化依次有序进行,确保每个区间可完全被污水覆盖进行反应,提高湿地利用率;
5.通过第一料框101、第二料框201、第三料框301与模块架7可拆卸式连接,实现湿地装置可拆卸安装且便于安装;
6.湿地堵塞时,通过沿水平方向滑动第二料框201,将第二料框201以及第三料框301暴露在外,方便对其内部的填料进行清洁。
应当理解本文所述的例子和实施方式仅为了说明,并不用于限制本发明,本领域技术人员可根据它做出各种修改或变化,凡在本发明的精神和原则之内,所作的任何修改、等同替换、改进等,均应包含在本发明的保护范围之内。
Claims (10)
- 一种阻水透气间歇曝气的模块式人工湿地,其特征在于,包括好氧反应区(1)、缺氧反应区(2)、土壤植物区(3)以及曝气管(4);所述好氧反应区(1)、所述缺氧反应区(2)以及所述土壤植物区(3)沿自下而上的出水方向依次连通,且所述好氧反应区(1)包括由内至外间隔设置的透气阻水层(5)和隔气层(6),所述曝气管(4)的曝气口位于所述透气阻水层(5)以及所述隔气层(6)围合的空腔内。
- 根据权利要求1所述的阻水透气间歇曝气的模块式人工湿地,其特征在于,还包括模块架(7)以及穿设在所述模块架(7)上的进水管(8),所述好氧反应区(1)还包括与所述模块架(7)间隔设置且与所述进水管(8)相连通的第一料框(101),所述曝气管(4)穿设在所述模块架(7)上且曝气口位于所述模块架(7)与所述第一料框(101)的间隙位置处,所述透气阻水层(5)设置在所述第一料框(101)上,所述隔气层(6)设置在所述模块架(7)上。
- 根据权利要求2所述的阻水透气间歇曝气的模块式人工湿地,其特征在于,所述缺氧反应区(2)至少包括第二料框(201),所述土壤植物区(3)至少包括第三料框(301),所述第二料框(201)以及所述第三料框(301)均可沿竖直方向与所述模块架(7)可拆卸式连接,且所述第二料框(201)还可沿水平方向与所述第一料框(101)以及所述第三料框(301)滑动密封连接。
- 根据权利要求3所述的阻水透气间歇曝气的模块式人工湿地,其特征在于,所述进水管(8)设置有至少四个主进水管口(801),且四个所述主进水管口(801)均匀的穿设在模块架(7)的四周。
- 根据权利要求3所述的阻水透气间歇曝气的模块式人工湿地,其特征在于,所述曝气管(4)设置有至少四个主进气管口(401),且四个所述主进气管口(401)均匀的穿设在模块架(7)的四周。
- 根据权利要求3至5中任一项所述的阻水透气间歇曝气的模块式人工湿 地,其特征在于,所述第二料框(201)的上下两侧分别沿竖直方向设置有第一凸缘(202)和第二凸缘(203),且所述第一凸缘(202)可沿水平方向与所述第二料框(201)滑动密封连接,所述第三料框(301)以及所述第一料框(101)上分别设置有与所述第一凸缘(202)以及所述第二凸缘(203)密封插接配合的第一凹槽体(302)和第二凹槽体(102),且所述第二凹槽体(102)可沿水平方向与所述第一料框(101)滑动密封连接。
- 根据权利要求6所述的阻水透气间歇曝气的模块式人工湿地,其特征在于,所述模块架(7)的两侧还分别沿竖直方向开设有限位滑槽(701),所述限位滑槽(701)内还转动设置有螺纹杆(9),所述螺纹杆(9)上还螺纹连接有两个滑块(10),且两个所述滑块(10)还分别与所述限位滑槽(701)的槽壁滑动连接;所述第二料框(201)的左右两侧还分别沿水平方向开设有第一滑槽(2011),两个所述第一滑槽(2011)内分别滑动设置有可在两个所述限位滑槽(701)内滑动的第一凸块(204),且所述第一凸块(204)可供所述螺纹杆(9)以及位于上方的所述滑块(10)穿过,且所述第一凸块(204)还可抵在位于下方的所述滑块(10)的顶端;所述第三料框(301)的两侧还分别设置有可在两个所述限位滑槽(701)内滑动第二凸块(303),且所述第二凸块(303)可供所述螺纹杆(9)穿过且可抵在位于上方的所述滑块(10)的顶端。
- 根据权利要求7所述的阻水透气间歇曝气的模块式人工湿地,其特征在于,所述第一凸块(204)包括块体(2041)、沿竖直方向滑动穿设在所述块体(2041)上的滑竿(2042)、两个分别沿水平方向滑动穿设在所述块体(2041)上的插块(2043)、设置在所述滑竿(2042)上且可控制两个所述插块(2043)沿同一方向同步滑动的驱动块(2044)以及绕设在所述滑竿(2042)上可将所述滑竿(2042)复位的弹簧(2045),且所述第一滑槽(2011)以及所述限位滑槽(701)的槽壁上还分别开设有可与所述插块(2043)插接配合的插槽(7011), 且所述滑竿(2042)还可与所述第二凸块(303)相抵。
- 根据权利要求8所述的阻水透气间歇曝气的模块式人工湿地,其特征在于,所述驱动块(2044)的截面呈平行四边形,两个所述插块(2043)的一侧分别呈倾斜状且分别与所述驱动块(2044)的两个倾斜面相接触,且两个插块(2043)还分别与所述驱动块(2044)通过连杆(2046)滑动铰接。
- 根据权利要求8所述的阻水透气间歇曝气的模块式人工湿地,其特征在于,所述模块架(7)内还设置有输出端与一个所述螺纹杆(9)相连接的电机(11),且两个所述螺纹杆(9)上均还设置有皮带轮(12),两个所述皮带轮(12)间还连接有皮带(13)。
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