CN201128703Y - subsurface flow alternate constructed wetland - Google Patents
subsurface flow alternate constructed wetland Download PDFInfo
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- CN201128703Y CN201128703Y CNU2007200230013U CN200720023001U CN201128703Y CN 201128703 Y CN201128703 Y CN 201128703Y CN U2007200230013 U CNU2007200230013 U CN U2007200230013U CN 200720023001 U CN200720023001 U CN 200720023001U CN 201128703 Y CN201128703 Y CN 201128703Y
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- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 32
- 241000196324 Embryophyta Species 0.000 claims description 15
- 239000002689 soil Substances 0.000 claims description 7
- 235000016791 Nymphaea odorata subsp odorata Nutrition 0.000 claims description 5
- 235000014676 Phragmites communis Nutrition 0.000 claims description 4
- 239000003415 peat Substances 0.000 claims description 3
- 244000025254 Cannabis sativa Species 0.000 claims description 2
- 241000209490 Nymphaea Species 0.000 claims description 2
- 241000746966 Zizania Species 0.000 claims description 2
- 241000195940 Bryophyta Species 0.000 claims 1
- 235000018994 Nuphar advena Nutrition 0.000 claims 1
- 244000020186 Nymphaea lutea Species 0.000 claims 1
- 241000245301 Nymphoides Species 0.000 claims 1
- 235000000476 Nymphoides peltata Nutrition 0.000 claims 1
- 240000001398 Typha domingensis Species 0.000 claims 1
- 235000002636 Zizania aquatica Nutrition 0.000 claims 1
- 239000010865 sewage Substances 0.000 abstract description 12
- 238000005192 partition Methods 0.000 abstract description 9
- 230000000694 effects Effects 0.000 abstract description 4
- 239000003344 environmental pollutant Substances 0.000 abstract description 4
- 229910001385 heavy metal Inorganic materials 0.000 abstract description 4
- 239000005416 organic matter Substances 0.000 abstract description 4
- 230000002093 peripheral effect Effects 0.000 abstract description 4
- 231100000719 pollutant Toxicity 0.000 abstract description 4
- 235000015097 nutrients Nutrition 0.000 abstract description 3
- 239000000126 substance Substances 0.000 abstract description 3
- 231100000331 toxic Toxicity 0.000 abstract description 3
- 230000002588 toxic effect Effects 0.000 abstract description 3
- 230000007613 environmental effect Effects 0.000 abstract 1
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 6
- 244000005700 microbiome Species 0.000 description 4
- 241000731961 Juncaceae Species 0.000 description 3
- 244000207740 Lemna minor Species 0.000 description 3
- 235000006439 Lemna minor Nutrition 0.000 description 3
- 241000209477 Nymphaeaceae Species 0.000 description 3
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 3
- 244000273256 Phragmites communis Species 0.000 description 3
- 235000001855 Portulaca oleracea Nutrition 0.000 description 3
- 241000233948 Typha Species 0.000 description 3
- 229910052757 nitrogen Inorganic materials 0.000 description 3
- 229910052698 phosphorus Inorganic materials 0.000 description 3
- 239000011574 phosphorus Substances 0.000 description 3
- 238000000746 purification Methods 0.000 description 3
- 238000004062 sedimentation Methods 0.000 description 3
- 241000255925 Diptera Species 0.000 description 2
- 238000005202 decontamination Methods 0.000 description 2
- 230000003588 decontaminative effect Effects 0.000 description 2
- 239000000945 filler Substances 0.000 description 2
- 238000001914 filtration Methods 0.000 description 2
- 238000000034 method Methods 0.000 description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 238000009395 breeding Methods 0.000 description 1
- 230000001488 breeding effect Effects 0.000 description 1
- DNJIEGIFACGWOD-UHFFFAOYSA-N ethanethiol Chemical compound CCS DNJIEGIFACGWOD-UHFFFAOYSA-N 0.000 description 1
- 239000011464 hollow brick Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 239000004033 plastic Substances 0.000 description 1
- 229920003023 plastic Polymers 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
Images
Classifications
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- 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
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- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
Abstract
本实用新型涉及一种潜表流交替人工湿地,包括湿地外围墙、进水池、出水池、进水口、出水口、潜流区域、表面流区域、间隔墙和湿地植物,湿地外围墙内左右两端分别设有进水池和出水池,靠近进、出水池处设有潜流区域,中间间隔墙设置潜流区域和表面流区域,潜流区域和表面流区域之间通过间隔墙分开,在左右两端的潜流区域上分别设有进水口和出水口,潜流区域和表面流区域上面分别种植有湿地植物。运行时,污水由进水口流入潜流区域,去除悬浮物质和溶解性污染物,再流经表面流区域,去除有机物,湿地植物吸收营养物质、重金属和有毒有害物质,净化后的污水由出水管排入出水池。其具有出水效果好、天气影响小、成本低、管理方便、安全环保等优点。
The utility model relates to an artificial wetland with alternating submerged and surface flow, which comprises a wetland peripheral wall, a water inlet pool, a water outlet pool, a water inlet, a water outlet, an undercurrent area, a surface flow area, a partition wall and wetland plants, and the left and right ends of the wetland peripheral wall There are respectively an inlet pool and an outlet pool. There is an underflow area near the inlet and outlet pools. The middle partition wall is provided with an underflow area and a surface flow area. The underflow area and the surface flow area are separated by a partition wall. There are water inlets and water outlets on the top, and wetland plants are planted on the subsurface flow area and the surface flow area. During operation, sewage flows into the subsurface flow area from the water inlet to remove suspended matter and dissolved pollutants, and then flows through the surface flow area to remove organic matter, wetland plants absorb nutrients, heavy metals and toxic and harmful substances, and the purified sewage is discharged from the outlet pipe In and out of the pool. It has the advantages of good water discharge effect, little weather influence, low cost, convenient management, safety and environmental protection, etc.
Description
技术领域 technical field
本实用新型涉及一种水质净化装备,具体地说是一种利用潜流和表面流人工湿地结合来处理净化污水的新型的潜表流交替人工湿地。The utility model relates to a water quality purification equipment, in particular to a novel subsurface-surface flow alternate artificial wetland which utilizes the combination of subsurface flow and surface flow artificial wetland to treat and purify sewage.
背景技术 Background technique
我们知道,人工湿地技术具有投资少、管理简单、成本低的优点,有良好的应用前景。人工湿地可分为表面流和潜流式两种类型,两者各有优缺点。潜流式床体,有机物、氮、磷和重金属等污染指标的去除效果好,且很少有恶臭和孳生蚊蝇现象,但由于氧的供给能力非常有限,且控制复杂,降低了水的净化效果;表面流人工湿地可对有机物进行好氧处理,缺点是占地面积大,水力负荷低,去污能力有限,出水中悬浮物较多,受气候影响较大,夏季会孽生蚊蝇、散发臭味。We know that constructed wetland technology has the advantages of less investment, simple management, and low cost, and has a good application prospect. Constructed wetlands can be divided into two types: surface flow and subsurface flow, both of which have advantages and disadvantages. The submerged flow bed has a good removal effect on pollution indicators such as organic matter, nitrogen, phosphorus and heavy metals, and there is little stench and breeding of mosquitoes and flies. However, due to the very limited oxygen supply capacity and complicated control, the water purification effect is reduced. ; The surface flow artificial wetland can carry out aerobic treatment of organic matter. The disadvantages are that it occupies a large area, low hydraulic load, limited decontamination capacity, and there are more suspended solids in the effluent, which is greatly affected by the climate. stink.
发明内容 Contents of the invention
本实用新型为克服上述现有技术的不足,提供一种结构简单、占地面积小、去污能力强、无异味、供养能力强的潜表流交替人工湿地。In order to overcome the shortcomings of the above-mentioned prior art, the utility model provides a subsurface-surface flow alternating artificial wetland with simple structure, small footprint, strong decontamination ability, no peculiar smell, and strong support ability.
本实用新型的目的是采用下述技术方案实现的:一种潜表流交替人工湿地,包括湿地外围墙、进水池、出水池、进水口、出水口、潜流区域、表面流区域、间隔墙和湿地植物,湿地外围墙内两端分别设有进水池和出水池,靠近进、出水池处设有潜流区域,中间间隔设置潜流区域和表面流区域,潜流区域和表面流区域之间通过间隔墙分开,在左右两端的潜流区域上分别设有进水口和出水口,潜流区域和表面流区域上面分别种植有水生植物。The purpose of this utility model is achieved by adopting the following technical solutions: a submerged surface flow alternate artificial wetland, including wetland peripheral wall, water inlet pool, water outlet pool, water inlet, water outlet, subsurface flow area, surface flow area, partition wall and Wetland plants, the two ends of the outer wall of the wetland are respectively provided with an inlet pool and an outlet pool, and there is an underflow area near the inlet and outlet pools, and an underflow area and a surface flow area are set in the middle, and the underflow area and the surface flow area are separated by a partition wall Separately, water inlets and water outlets are respectively arranged on the subsurface flow areas at the left and right ends, and aquatic plants are respectively planted on the subsurface flow areas and the surface flow areas.
所述的潜流区域由上到下依次为湿地植物、砾石层和覆土层。The subsurface flow area includes wetland plants, gravel layer and overburden layer from top to bottom.
所述的进水口位于砾石层的上部,出水口位于砾石层下中部。The water inlet is located at the upper part of the gravel layer, and the water outlet is located at the lower middle of the gravel layer.
所述的潜流区的覆土层和整个表面流区域由田园土和草炭构成。The covering soil layer of the subsurface flow zone and the entire surface flow area are composed of pastoral soil and peat.
所述的潜流区域的覆土层厚10-15cmThe covering soil layer in the subsurface flow area is 10-15cm thick
所述的间隔墙上设有小孔。Small holes are arranged on the partition wall.
所述的水生植物是菰草、香蒲、芦苇、灯心草、萍蓬草、荇菜和睡莲中的一种或多种。The aquatic plants are one or more of wild rice plants, cattails, reeds, rushes, duckweeds, water lilies and water lilies.
本实用新型运行时,污水经进水池由进水口流入潜流区域,进水中的悬浮物质通过砾石层的沉积和过滤作用快速去除,溶解性污染物主要是依靠填料和根系表面附着生长微生物的作用去除,再流经表面流区域,在此区域有机物的去除主要依靠水面近乎静止沉淀的条件和表面茎杆附着的微生物的作用。潜流区和表面流区域中种植的湿地植物可直接吸收污水中氮、磷等营养物质、重金属和有毒有害物质,并将其转化,转变成植物的组分。最后,净化后的污水由湿地右端两个出水口排入出水池。When the utility model is in operation, the sewage flows into the underflow area from the water inlet through the water inlet pool, and the suspended matter in the water inlet is quickly removed through the sedimentation and filtration of the gravel layer, and the soluble pollutants mainly rely on the growth of microorganisms attached to the surface of the filler and the root system Remove, and then flow through the surface flow area, where the removal of organic matter mainly depends on the near-stationary sedimentation conditions on the water surface and the action of microorganisms attached to the surface stems. The wetland plants planted in the subsurface flow area and the surface flow area can directly absorb nutrients such as nitrogen and phosphorus, heavy metals and toxic and harmful substances in sewage, and transform them into plant components. Finally, the purified sewage is discharged into the effluent pool from the two outlets at the right end of the wetland.
本实用新型的优点如下:The utility model has the following advantages:
1.克服了潜流式人工湿地和表面流人工湿地的缺点,使二者有机结合到一起,出水效果较好;1. It overcomes the shortcomings of subsurface flow constructed wetland and surface flow constructed wetland, and makes the two organically combined to achieve better water discharge effect;
2.受天气情况影响较小,可连续运行;2. It is less affected by weather conditions and can run continuously;
3.投资少,设备简单,管理方便,污水处理成本较低;3. Less investment, simple equipment, convenient management, and low cost of sewage treatment;
4.整个处理工艺安全环保,无二次污染。4. The whole treatment process is safe and environmentally friendly, without secondary pollution.
附图说明 Description of drawings
图1是本实用新型结构示意图;Fig. 1 is a structural representation of the utility model;
图2是图1的俯视图;Fig. 2 is the top view of Fig. 1;
其中1.进水管,2、砾石层,3.表面流区域,4.出水管,5.覆土层,6.水生植物,7.潜流区域,8.间隔墙,9.湿地外围墙,10.进水池,11.出水池。1. Inlet pipe, 2. Gravel layer, 3. Surface flow area, 4. Outlet pipe, 5. Overburden layer, 6. Aquatic plants, 7. Subsurface flow area, 8. Partition wall, 9. Wetland peripheral wall, 10. Into the pool, 11. Out of the pool.
具体实施方式 Detailed ways
下面结合附图和实施例对本实用新型进一步说明。Below in conjunction with accompanying drawing and embodiment the utility model is further described.
图1、图2中,人工湿地外围墙9可用混凝土构成,进水管1和出水管4可嵌入其中,潜流区域7竖直方向分为砾石层2和覆土层5,进水管口位于砾石层2的上部,出水管口位于砾石层2下中部,潜流区域7和表面流区域3相接的可用混凝土制成,上部的间隔墙8可用空心砖或带孔PVC塑料制成,潜流区域7的覆土层5和整个表面流区域3由田园土和草炭构成,其上可种植菰草、香蒲、芦苇、灯心草、萍蓬草、荇菜、睡莲等湿地植物6。其中潜流区域7的覆土层5厚约10-15cmIn Fig. 1 and Fig. 2, the
水质净化处理时,污水从进水池10由两个进水管1均匀布水流入潜流区域7,污水在砾石层2内部渗流,进水中的悬浮物质通过砾石层2的沉积和过滤作用快速去除,溶解性污染物主要是依靠填料和根系表面附着生长微生物的作用去除,污水由潜地流区域7右端经间隔墙8的小孔流入表面流区域3,在表面流区域中污染物主要通过床体中植物、微生物的综合作用去除,污水由表面流区域3流出后,再依次流经潜流区域7、表面流区域3和潜流区域7。潜流区域7和表面流区域3中种植的菰草、香蒲、芦苇、灯心草、萍蓬草、荇菜、睡莲等水生植物6可直接吸收污水中可利用态的氮、磷等营养物质、重金属和有毒有害物质,并将其转化、转变成植物的组分。最后,净化后的污水由湿地右端两个出水管4排入出水池11。During the water purification treatment, the sewage is evenly distributed into the
Claims (7)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CNU2007200230013U CN201128703Y (en) | 2007-06-01 | 2007-06-01 | subsurface flow alternate constructed wetland |
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| CNU2007200230013U CN201128703Y (en) | 2007-06-01 | 2007-06-01 | subsurface flow alternate constructed wetland |
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| CN201128703Y true CN201128703Y (en) | 2008-10-08 |
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Cited By (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101973635A (en) * | 2010-09-21 | 2011-02-16 | 常州大学 | Method for efficiently purifying heavy metal polluted wastewater by combining wetland plant |
| CN104556377A (en) * | 2014-12-15 | 2015-04-29 | 上海交通大学 | Method for improving nitrogen removal efficiency of low-pollution water body with low carbon nitrogen ratio |
| CN105906067A (en) * | 2016-06-21 | 2016-08-31 | 山东建筑大学 | High and low ridge type artificial wetland capable of being constructed in modular mode |
| CN106396295A (en) * | 2016-12-06 | 2017-02-15 | 广西壮族自治区农业科学院农业资源与环境研究所 | Device for treating pig raising wastewater by using myriophyllum spicatum |
| CN110510746A (en) * | 2019-08-30 | 2019-11-29 | 中国水利水电科学研究院 | Constructed wetland device |
| CN111943432A (en) * | 2020-08-11 | 2020-11-17 | 湖南艾布鲁环保科技股份有限公司 | Lake or reservoir drinking water source pollution prevention and control system and method |
-
2007
- 2007-06-01 CN CNU2007200230013U patent/CN201128703Y/en not_active Expired - Fee Related
Cited By (9)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101973635A (en) * | 2010-09-21 | 2011-02-16 | 常州大学 | Method for efficiently purifying heavy metal polluted wastewater by combining wetland plant |
| CN101973635B (en) * | 2010-09-21 | 2012-11-28 | 常州大学 | Method for efficiently purifying heavy metal polluted wastewater by combining wetland plant |
| CN104556377A (en) * | 2014-12-15 | 2015-04-29 | 上海交通大学 | Method for improving nitrogen removal efficiency of low-pollution water body with low carbon nitrogen ratio |
| CN105906067A (en) * | 2016-06-21 | 2016-08-31 | 山东建筑大学 | High and low ridge type artificial wetland capable of being constructed in modular mode |
| CN106396295A (en) * | 2016-12-06 | 2017-02-15 | 广西壮族自治区农业科学院农业资源与环境研究所 | Device for treating pig raising wastewater by using myriophyllum spicatum |
| CN110510746A (en) * | 2019-08-30 | 2019-11-29 | 中国水利水电科学研究院 | Constructed wetland device |
| CN110510746B (en) * | 2019-08-30 | 2020-04-21 | 中国水利水电科学研究院 | Constructed Wetland Device |
| CN111943432A (en) * | 2020-08-11 | 2020-11-17 | 湖南艾布鲁环保科技股份有限公司 | Lake or reservoir drinking water source pollution prevention and control system and method |
| CN111943432B (en) * | 2020-08-11 | 2021-08-24 | 湖南艾布鲁环保科技股份有限公司 | Lake or reservoir drinking water source pollution prevention and control system and method |
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Legal Events
| Date | Code | Title | Description |
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| C14 | Grant of patent or utility model | ||
| GR01 | Patent grant | ||
| C17 | Cessation of patent right | ||
| CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20081008 Termination date: 20110601 |