CN2844109Y - Artificial wet-land sewage-water treater of zeolite and limestone - Google Patents
Artificial wet-land sewage-water treater of zeolite and limestone Download PDFInfo
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- CN2844109Y CN2844109Y CN 200520143198 CN200520143198U CN2844109Y CN 2844109 Y CN2844109 Y CN 2844109Y CN 200520143198 CN200520143198 CN 200520143198 CN 200520143198 U CN200520143198 U CN 200520143198U CN 2844109 Y CN2844109 Y CN 2844109Y
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- partition wall
- zeolite
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- water
- wet land
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Abstract
The utility model discloses an artificial wet land sewage water treatment device of zeolite and limestone. A vertical composite flow artificial wet land is used, the middle upper part of a wet land pool (7) is provided with a partition wall (3), the upper part of one edge of the partition wall (3) is provided with a water inlet pipe (1), and the upper part of the other edge of the partition wall (3) is provided with a water outlet pipe (5). The sequence of filling materials in the wet land pool is that the bottom is filled with cobble filling material (9), mixing filling material (8) of the zeolite and the limestone is arranged on the cobble filling material (9), and a quartz fine sand layer (2) is laid at the top; plants (4) are planted on the upper surface of the quartz fine sand layer (2). The plants (4) form various plant beds using India cannas as the main body, elephant grasses, acorus calamus and zizania aquatica grasses are alternatively planted in a mixing way, and plant root systems (6) are penetrated into the cobble layer (9) at the bottom. The utility model has the advantages of shock resistance loading capacity, convenient follow-up maintenance operation, simple investment and construction, etc. The purpose of deeply treating the outlet water of city sewage water treating plants is effectively realized, and the utility model has the value of beautifying landscape and has no secondary pollution.
Description
Technical field
The present invention relates to waste disposal plant, particularly the waste disposal plant of zeolite and the water outlet of Wingdale artificial swamp Treating Municipal Sewage treatment plant.
Background technology
Because the shortage of water resources, both at home and abroad more and more widely to the research of sewage recycling process.The reusing sewage technology mainly contains coagulating sedimentation, advanced oxidation, disinfection by ultraviolet light, charcoal absorption and membrane filtration technique etc. at present, but because the use of coagulating agent in traditional coagulation sedimentation method cause secondary pollution easily, and treatment effect is general; And advanced oxidation, disinfection by ultraviolet light, charcoal absorption and membrane filtration technique etc. are higher owing to processing cost, and the running maintenance complexity, are difficult to be promoted the use of widely.
Summary of the invention
The purpose of this utility model provides a kind of zeolite and Wingdale of utilizing for the main body filler and plant preferred four kinds of wetland plants, effluent of municipal sewage plant is carried out the waste disposal plant of advanced treatment.
The present invention is achieved in that and sets up an artificial swamp pond, and there is a partition wall middle and upper part, wetland pond, and a water inlet pipe is arranged at the top, one side of partition wall, and a rising pipe is arranged at the other side top of partition wall.Filling filler in the pond, the filler fill order is: bottom filling particle diameter is that the pebbles of 40~80mm is crossed water layer thickness 10~30cm, be that particle diameter is zeolite and the Wingdale mixed fillers of 4~8mm on it, volume ratio is 1: 1, thickness is 50~80cm, the quartzy fine sand layer that particle diameter is 1~2mm is filled out in the shop, top, and thickness is 10~20cm.Plant above the quartzy fine sand layer plant is arranged, various plants bed based on Canna generalis Bailey, between mix with napier grass, calamus and hay grass and to take plantation, planting density be 38~40 strains/square metre, Canna generalis Bailey: napier grass: calamus: its planting proportion of hay grass is 4~8: 1~2: 4~8: 1~2; The root system of plant is deeply to bottom pebbles layer.
Fluidised form adopts vertical compound flow constructed wetland, and to the water inlet of stream cell surface, current direction is flowed to bottom pebbles water conservancy diversion layer, and then flows into the upward flow unit down through the main body packing layer current by down, and current are discharged by its top.
Reach " urban sewage reutilization water for scenic environment use water quality " (GB/T 18921-2002) standard through main water-quality guideline such as ammonia nitrogen, total phosphorus, COD and BOD in the artificial swamp processing back water outlet.
The utility model adopts artificial swamp that effluent of municipal sewage plant is carried out advanced treatment, have that treatment effect is good, processing efficiency is high, the shock resistance compound ability is strong, stable, the investment working cost is low, convenient management, advantage such as both artistic and practical, has development prospect preferably, suitable promoting the use of.Adopt the plant bed vertical combined-flow simulation artificial wet land treating system of Canna generalis Bailey that sewage disposal plant effluent is carried out advanced treatment, can remove pollutents such as nitrogen phosphorus effectively, thereby prevent the eutrophication of water body effectively, its water outlet also can be used for the view reuse.
Description of drawings
Fig. 1 simulates the constructed wetland device synoptic diagram for the utility model embodiment.
Fig. 2 is the treatment effect figure of the utility model embodiment to COD.
Fig. 3 is the treatment effect figure of the utility model embodiment to ammonia nitrogen.
Fig. 4 is the treatment effect figure of the utility model embodiment to total phosphorus.
Fig. 5 is the treatment effect figure of the utility model embodiment to BOD.
Mark among Fig. 1: 1. water inlet pipe, 2. quartzy fine sand layer, 3. partition wall, 4-wetland plant, 5. rising pipe, 6. root system of plant, 7. wetland pond, 8. zeolite limestone filler, 9. pebbles filler.
Embodiment
Embodiment
As shown in Figure 1, artificial swamp pond (7), surface size is 1.0m * 0.5m, highly is 1.0m, and the filler porosity is 40%, and useful volume is 200L, and residence time 24h, hydraulic load are 0.4m
3/ (m
2D).There is a partition wall middle and upper part, wetland pond, and wetland pond (7) and partition wall (3) are made by plastic plate; One water inlet pipe (1) is arranged at the top, one side of partition wall (3), and a rising pipe (5) is arranged at the other side top of partition wall (3).Filling filler in the pond, the filler general thickness is 100cm, the filler fill order is: bottom filling particle diameter is that the pebbles filler (9) of 40~80mm is crossed water layer thickness 10cm, be that particle diameter is zeolite and the Wingdale mixed fillers (8) of 4~8mm on it, volume ratio is 1: 1, thickness is 80cm, and the quartzy fine sand layer (2) that particle diameter is 1~2mm is filled out in the shop, top, and thickness is 10cm.Planting above the quartzy fine sand layer (2) has plant (4), based on the various plants bed of Canna generalis Bailey, and with napier grass, calamus with the hay grass is mixed takes plantation, Canna generalis Bailey, napier grass, calamus, the hay grass is planted 8,2,8,2 respectively; Root system of plant (6) is deeply to bottom pebbles layer (9).
Adopt vertical compound flow constructed wetland, to the water inlet of stream cell surface, current direction is flowed to bottom pebbles water conservancy diversion layer, and then flows into the upward flow unit down through the main body packing layer current by down, and current are discharged by its top.
Effluent quality after raw water quality and process native system are handled sees Table 1.
Table 1 sewage quality table
Water-quality guideline | pH | CODcr(mg/L) | BOD 5(mg/L) | Total phosphorus (mg/L) | Ammonia nitrogen (mg/L) |
Water inlet | 6.8~7.0 | 14.4~32.40 | 2.34~9.93 | 0.30~3.85 | 1.37~18.99 |
Water outlet | 6.5~7.5 | 6.56~19.75 | 0.19~2.71 | 0.01~0.49 | 0.01~4.80 |
National standard * | 6~9 | 20 | 4 | 0.5 | 5 |
* be " urban sewage reutilization water for scenic environment use water quality " (GB/T 18921-2002) standard
Adopt 24 hours continuous water intake modes, intaking is effluent of municipal sewage plant.The residence time is 24h, and hydraulic load is 0.4m
3/ (m
2D).Experimental result through system's steady running in continuous 9 months shows: this zeolite Wingdale simulation artificial wet land treating system can effectively be removed ammonia nitrogen, total phosphorus, COD and BOD, and treatment effect is seen Fig. 2, Fig. 3, Fig. 4, Fig. 5 respectively.
During 9 months steady running, when the content of COD, ammonia nitrogen, total phosphorus and BOD is respectively 14.40~32.40mg/L, 1.37~18.99mg/L, 0.30~3.85mg/L and 2.34~9.93mg/L in the water inlet, handle that the every Pollutant levels in back are reduced to 6.56~19.75 respectively, 0.01~4.80mg/L, 0.01~0.49mg/L and 0.19~2.71mg/L, leading indicator satisfies " urban sewage reutilization water for scenic environment use water quality " (GB/T 18921-2002) standard-required.
Reach " urban sewage reutilization water for scenic environment use water quality " (GB/T 18921-2002) standard through main water-quality guideline such as ammonia nitrogen, total phosphorus, COD and BOD in the artificial swamp processing back water outlet.
Claims (1)
1. zeolite and Wingdale artificial wet field facilities for treating sewage, comprise wetland pond (7), partition wall (3), water inlet pipe (1), rising pipe (5), it is characterized in that adopting vertical compound flow constructed wetland, there is a partition wall (3) middle and upper part, wetland pond (7), one water inlet pipe (1) is arranged at the top, one side of partition wall (3), and a rising pipe (5) is arranged at the other side top of partition wall (3); Filling filler in the pond, the filler fill order is: pebbles filler (9) is filled in the bottom, is zeolite and Wingdale mixed fillers (8) on it, and rockfill English fine sand layer (2) shop, top; Planting above the quartzy fine sand layer (2) has plant (4), and plant (4) is based on the various plants bed of Canna generalis Bailey, takes plantation so that napier grass, calamus and hay grass are mixed; Root system of plant (6) is deeply to bottom pebbles layer (9).
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
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CN 200520143198 CN2844109Y (en) | 2005-11-18 | 2005-11-18 | Artificial wet-land sewage-water treater of zeolite and limestone |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN 200520143198 CN2844109Y (en) | 2005-11-18 | 2005-11-18 | Artificial wet-land sewage-water treater of zeolite and limestone |
Publications (1)
Publication Number | Publication Date |
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CN2844109Y true CN2844109Y (en) | 2006-12-06 |
Family
ID=37486061
Family Applications (1)
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CN 200520143198 Expired - Fee Related CN2844109Y (en) | 2005-11-18 | 2005-11-18 | Artificial wet-land sewage-water treater of zeolite and limestone |
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Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN113353903A (en) * | 2021-06-10 | 2021-09-07 | 暨南大学 | Preparation method of hydroxyapatite and constructed wetland system constructed by same |
-
2005
- 2005-11-18 CN CN 200520143198 patent/CN2844109Y/en not_active Expired - Fee Related
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN113353903A (en) * | 2021-06-10 | 2021-09-07 | 暨南大学 | Preparation method of hydroxyapatite and constructed wetland system constructed by same |
CN113353903B (en) * | 2021-06-10 | 2024-02-09 | 暨南大学 | Preparation method of hydroxyapatite and constructed wetland system thereof |
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GR01 | Patent grant | ||
C19 | Lapse of patent right due to non-payment of the annual fee | ||
CF01 | Termination of patent right due to non-payment of annual fee |