CN102910736A - Construction technology of ecological sewage discharging ditch - Google Patents
Construction technology of ecological sewage discharging ditch Download PDFInfo
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- CN102910736A CN102910736A CN2011102234147A CN201110223414A CN102910736A CN 102910736 A CN102910736 A CN 102910736A CN 2011102234147 A CN2011102234147 A CN 2011102234147A CN 201110223414 A CN201110223414 A CN 201110223414A CN 102910736 A CN102910736 A CN 102910736A
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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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Abstract
The invention relates to a construction technology of an ecological sewage discharging ditch, belongs to the field of wastewater treatment, in particular to a construction technology of an ecological purification process aiming at rural wastewater. The construction technology comprises the steps of constructing a ditch body (1), manufacturing vegetated substrate bag bodies (2) and water sucking bands (5), selecting purification plants (4) and artificial substrate materials (3), filling the artificial substrate (3), planting seedlings of purification plants (4), maintaining a vegetated substrate bag unit, and installing and fixing. According to the construction technology of the ecological sewage discharging ditch, an ecological wastewater treatment system can be fast constructed, so that the construction difficulty of a wastewater collecting pipe network and the defect of the traditional wastewater treatment process are greatly overcome. The construction technology is especially suitable for popularization and use in dispersive places of rural wastewater discharge of remote and border areas and mountain areas and the Karst region.
Description
Affiliated technical field
The present invention relates to a kind of ecological blowdown ditch building technology, belong to sewage treatment area, especially for the ecological purification technique building technology of Rural Waste Water.
Background technology
Wash away the rainwash of generation, high density percolate that dumping produces, peasant household's cultivation (chicken and duck and pig ox) livestock and poultry uncontrollable discharge behind the sanitary wastewater that Rural Waste Water mainly produces from every family (kitchen washing draining, the daily laundrywastes of washing one's face and rinsing one's mouth, garden wash-down water), colony house cultivation and lavatory draining, garden and the road rain and wash away the sewage, farmland production (growing vegetables of high rich water etc.) efflux wastewater etc. of generation through water.Contain the organism such as Mierocrystalline cellulose, starch, carbohydrate, fat, protein in the Rural Waste Water, also be rich in the inorganic nutrients salts such as nitrogen, phosphorus, microbe species is abundant, and contains multiple pathogenic bacteria.Rural Waste Water has a large capacity and a wide range, discharges dispersion, organic concentration is low, and it is a difficult problem that faces in the new countryside construction that Rural Waste Water is administered.For Rural areas sparsely populated, that economy falls behind relatively, particularly remote border area, mountain area and karst region, because special economic condition, being uneven of geology and geomorphology and physical features, can't lay on a large scale pipe network or lay the pipe network cost high, and because relief is larger, lives and relatively disperse, Rural Waste Water is difficult to effectively collect and the more pumping equipment of needs and energy consumption.Fall behind in the Rural areas Economic development, per capita income is lower, and in the few situation of arable area, the laying of traditional sewage collecting pipe network and sewage pumping equipment and operation and maintenance cost are for the Rural areas is difficult to accept.
The city domestic sewage concentrated relative to the whole nation processed present situation and compared, the Rural Waste Water in current China overwhelming majority area still is in the state of letting drift, the processing rate of Rural Waste Water is extremely low, according to statistics, the domestic sewage in rural areas by using more than 95% or ight soil draining directly are discharged into underground or rivers,lakes and seas.Therefore, in recent years, the pollution effect of Rural Waste Water has surmounted the scope of local and point source, develops into basin-wide pollution problem, brings very big impact for the water body environmental capacity.
The normal method that adopts of existing dirty water living creature processing technique has anaerobic biological treatment, activated sludge process, biomembrance process etc.Its principal character is particularly bacterium of using microbe, and for giving full play in the custom-designed biochemical reactor of microbial process, the pollutent in the waste water is converted into microorganism cells and simple inorganics.In existing sewage disposal, brought into play vital role.Anaerobic biological treatment is mainly for the processing that is applicable to high concentrated organic wastewater, the residence time is longer, all kinds of Pollutant levels are still higher in the water outlet, and the Rural Waste Water organic content is totally lower, just so that anaerobic biological treatment is processed in Rural Waste Water great limitation arranged.Activated sludge process is the topmost method of conventional B-grade sewage treatment plant, and conventional B-grade sewage treatment plant pollutes at the control Sewage Environment is also having significant limitation aspect the control.At first the weakness of this method maximum is to produce a large amount of active sludge, and active sludge will cause serious secondary pollution as can not get effective processing, and excess sludge has become the bottleneck of activated sludge process development.Secondly it can only effectively be removed in biodegradable organism (usually with BOD), and can not effectively remove the organism (usually in COD) of difficult degradation, more can not effectively remove the trophicity salt such as nitrogen, phosphorus.The many subsequent processes of processing as anerobic sowage of biomembrance process are in order to improve water quality.The membrane bioreactor design and operation is simple, technical maturity, but use all is difficult to obtain good treatment effect separately, but mainly have at present the problems such as running cost is higher, system's running maintenance is comparatively complicated.
Existing ecological wastewater processing technology mainly is land treatment system, wherein artificial wet land treating system particularly, make up artificial ecosystem by matrix, plant, microorganism and process all kinds of waste water, become the focus of present stage research and main research direction, played an increasingly important role aspect processing sanitary sewage and the agricultural effluent.And also there are many limitations in actual applications in artificial swamp, the processing of conventional artificial swamp load only have conventional treatment method 1/10 or lower, thereby floor space is huge, China's land resources is very nervous, can't utilize.Secondly weather condition have a strong impact on artificial swamp, rainy season flood, winter low temperature all has a strong impact on the normal operation of artificial swamp.Again, easily produce alluvial, latch up phenomenon.
Sparsely populated in conjunction with Rural areas population, peasant's per capita income is low, Special Circumstances such as frontier area, mountain area and karst region particularly are so that the processing of Rural Waste Water faces technical problem and the economic problems of more complexity.And the Rural Waste Water discharging comparatively disperses, and water quality and quantity changes characteristics greatly, causes traditional sewage collecting and processing mode technically and all is difficult to economically solve the Rural Waste Water pollution problem.
Summary of the invention
In order to overcome the deficiency of Rural Waste Water sewage collecting pipeline network construction difficulty and existing saprobia, Ecological Disposal technique.The present invention proposes a kind of new ecological wastewater processing building technology, can the rapid build sewage ecological treatment system, particularly process on the spot for the Rural Waste Water of side area, mountain area and karst region is distributed.
Patent of the present invention solves the technical scheme that its technical problem adopts:
The present invention is a kind of ecological blowdown ditch building technology, comprises building the ditch body, makes plant substrates bag and suction band, selects purifying plant and artificial substratum material, and the maintenance of plant substrates bag is installed fixing.Its concrete steps are as follows: at first, according to physical features, select the existing blowdown ditch in rural area (soil property, cement, pile up etc.) or newly-built, along with water (flow) direction, drop arranges overfall and siphon drainage pipe during greater than 50cm.
Secondly, selection has better physical strength, closely knit, saturating property is good, and does not affect material that root system of plant penetrates as the bag containing soilless substrate material, the bag containing soilless substrate size, according to the plant growth characteristics of selecting, determine the significant depth of bag containing soilless substrate, be advisable not affect plant normal growth, general significant depth is at 20cm-50cm, for ease of making, maintenance, carrying, installation, generally be advisable at 1m-2m.The selection water absorbing properties is good, and the material that certain physical strength arranged is as the material of suction band, the suction stripe size, and the degree of depth can guarantee that length and bag containing soilless substrate size are identical in normal draws water in low water season.The suction band is made the side in the bag containing soilless substrate outside.
Again, select collocation rye grass, annual bluegrass, oat, garden sorrel, water harmony dish, Chinese celery, Canna generalis Bailey, parasol grass, again power flower and suitable native country species one or more, make up the sewage purification plant community.The option table area is large, and voidage is high, water absorbing properties good, and biological activity is high, chemical composition stability, and nontoxic material is as substrate material.
At last, load substrate material in bag containing soilless substrate, serike is made into matrix plant bag unit.In periphery pond, rural area, rivers and lakes or structures, cultivate.Cultured matrix plant bag unit is fixed in the side bilge both sides field assembly of building, be sewed with a side of suction band near the side bilge body of wall, matrix plant unit 1/2 depth and the long-term water level of side bilge maintain an equal level.
The beneficial effect of patent of the present invention is, can the rapid build sewage ecological treatment system, preferably resolve the deficiency of sewage collecting pipeline network construction difficulty and traditional waste water treatment process.And Rural Waste Water is in the process of ecological blowdown ditch of flowing through, the root system filtration that grows by both sides matrix plant bag, absorption, matrix absorption, microbial life mechanism and adsorption own, make organism, ammonia nitrogen, total nitrogen, suspended substance, turbidity, the colourity in the waste water and smell the flavor removed, simultaneously the pollution substances such as the nitrogen in the waste water, phosphorus and organism are converted into plant and animal microorganism nutritive substance, be converted into the cash crop such as herbage, vegetables and flowers and offer the villager, in addition, the rural area surrounding enviroment have also been beautified.
Description of drawings
Below in conjunction with drawings and Examples patent of the present invention is further specified.
Fig. 1 is ecological blowdown groove structure diagram of the present invention;
Fig. 2 is ecological blowdown ditch vertical view of the present invention;
Fig. 3 is plant substrates bag unit structural diagrams of the present invention;
Fig. 4 is the vertical view of Fig. 3.
1. pond bodies among the figure, 2. matrix bag, 3. artificial substratum, 4. purifying plant, 5. suction band, 6. fixed orifices, 7. point of fixity position, 8. sanitary sewage, the 9. long-term water level of sewage, 10. overfall, 11. siphon drainage pipes.
Embodiment
With reference to figure 1, Fig. 2, Fig. 3, the specific embodiment of the present invention is:
This ecology blowdown ditch building technology, comprise and build ditch body (1), make plant substrates bag (2) and suction band (5), select purifying plant (4) and artificial substratum material (3), artificial substratum (3) filling and the plantation of purifying plant plant (4) seedling, the maintenance of plant substrates bag unit is installed fixing.Its concrete steps are as follows: at first, according to physical features, select the existing blowdown ditch in rural area (soil property, cement, pile up etc.) or newly-built as pond body (1), wherein, along with water (flow) direction, drop arranges overfall (10) and siphon drainage pipe (11) during greater than 50cm.
Secondly, selecting has better physical strength, and closely knit, saturating property is good, and does not affect material that root system of plant penetrates as matrix bag (2) material.Wherein, plant substrates bag unit size is according to the plant growth characteristics of selecting, determine the significant depth of plant substrates bag unit, be advisable not affect plant normal growth, general significant depth is at 20cm-50cm, for ease of making, maintenance, carrying, installation, generally be advisable at 1m-2m.The selection water absorbing properties is good, the material of certain physical strength is arranged as the material of suction band (5).The stripe size that wherein absorbs water, the degree of depth can guarantee that length and plant substrates bag unit size are coincide in normal draws water in low water season.Suction band (5) is made the side in the plant substrates bag unit outside.
Again, one or more purifying plants (4) in the conventional sewage purification species that select the collocation humidogene, like fertile resistant, wastewater purifying efficiency are good or the suitable native country species make up the sewage purification plant community.The option table area is large, and voidage is high, water absorbing properties good, and biological activity is high, chemical composition stability, and nontoxic material is as artificial substratum (3) material.
At last, filling artificial substratum (3) in matrix bag (2), plantation purifying plant (4) seedling is made into matrix plant bag unit.In periphery pond, rural area, rivers and lakes or structures, cultivate.Cultured matrix plant bag unit is fixed in side bilge pond body (1) the both sides field assembly of building.Wherein, be sewed with a side of suction band (5) near pond body (1) body of wall, matrix plant bag unit 1/2 depth and the long-term water level of sewage (9) maintain an equal level.
The present invention can be by following experimental result proved to the treatment effect of Rural Waste Water.
Set up the open ecological blowdown ditch treatment system of a cover.The long 3m of blowdown ditch ditch body, wide 0.7m, dark 0.4m, the gradient 45 degree.Collocation plantation mater convolvulus, cyperus alternifolius, again power flower, Canna generalis Bailey, Brooks, cattail adopt slag as matrix, and intaking is school life's residential quarter externally discharged waste water, and daily influent load is 20-30L*d
-1* m
-2D after treatment system enters stationary phase, measures 9-12 month wastewater treatment efficiency, and system's treatment effect sees Table 1:
The open ecological blowdown ditch treatment system of table 1 is to the removal effect of principal pollutant
Found out by table 1, in period, there be extraordinary treatment effect in system to ammonia nitrogen and turbidity at this section at the beginning of winter late summer, average out to 96.6% and 97%, and also removal effect is more stable, maintains more than 93%.Removal effect to TP and COD is slightly poor, remove simultaneously luffing larger, but average removal rate has also all reached more than 77%, when effect is better, TP reaches 98%, the COD clearance also can also have this experiment just to simulate 3 meters ecological blowdown ditch near 90%, and actual blowdown ditch generally can both reach tens and arrive hundreds of rice, can reach reasonable removal effect to TP and COD.Simultaneity factor can improve the water outlet dissolved oxygen, is into the 5-7 of water doubly, reduce water inlet specific conductivity (EC) 2-3 doubly, smell the reduction that flavor also has certain degree, water inlet has quite strong stink, water outlet can't smell any smell, has improved preferably influent quality.In conjunction with country practical, long tens meters blowdown ditches to hundreds of rice are arranged.Along with the prolongation of ecological ditch, decontamination effect improving can further be strengthened.
The according to the above description announcement of book and instruction, those skilled in the art in the invention can also change and revise above-mentioned embodiment.Therefore, the embodiment that discloses and describe above the present invention is not limited to also should fall in the protection domain of claim of the present invention modifications and changes more of the present invention.In addition, although used some specific terms in this specification sheets, these terms do not consist of any restriction to the present invention just for convenience of description.
Claims (8)
1. ecological blowdown ditch building technology, it is characterized in that, comprise and build ditch body (1), make plant substrates bag (2) and suction band (5), select purifying plant (4) and artificial substratum material (3), artificial substratum (3) filling and the plantation of purifying plant (4) seedling, the maintenance of plant substrates bag unit, install fixing, by using the plant substrates bag unit, in the blowdown ditch, make up ecological sewage purifying system, realize nitrogen phosphorus organism turbidity and the removal of smelling flavor in the Rural Waste Water; Its concrete steps are as follows: at first, according to physical features, select the existing blowdown ditch in rural area (soil property, cement, pile up etc.) or newly-built as pond body (1); Secondly, selection has better physical strength, and closely knit, saturating property is good, and does not affect the material that root system of plant penetrates and make bag containing soilless substrate as matrix bag (2) material, the selection water absorbing properties is good, has the material of certain physical strength to make suction band (5) as water-absorbing material; Again, select artificial substratum, collocation purifying plant (4) makes up the sewage purification plant community; At last, filling artificial substratum (3) in matrix bag (2), plantation purifying plant (4) seedling is made into matrix plant bag unit; In periphery pond, rural area, rivers and lakes or structures, cultivate; Cultured matrix plant bag unit is fixed in side bilge pond body (1) both sides field assembly.
2. a kind of ecological blowdown ditch building technology according to claim 1 is characterized in that: ecological blowdown ditch is along with water (flow) direction, and drop arranges overfall (10) and siphon drainage pipe (11) during greater than 50cm.
3. according to right 1 described a kind of ecological blowdown ditch building technology, it is characterized in that: plant substrates bag unit size, according to the plant growth characteristics of selecting, determine the significant depth of plant substrates bag unit, be advisable not affect plant normal growth, general significant depth, generally is advisable at 1m-2m for ease of making, maintenance, carrying, installation at 20cm-50cm.
4. according to right 1 described a kind of ecological blowdown ditch building technology, it is characterized in that: suction stripe size, the degree of depth can guarantee that in normal draws water in low water season, length and plant substrates bag unit size are identical.Suction band (5) is made the side in the plant substrates bag unit outside.
5. according to right 1 described a kind of ecological blowdown ditch building technology, it is characterized in that: matrix plant bag unit is fixing in the assembling of side bilge pond body (1) both sides.
6. according to right 5 described a kind of ecological blowdown ditch building technologies, it is characterized in that: be sewed with a side of suction band (5) near pond body (1) body of wall, matrix plant bag unit 1/2 depth and the long-term water level of sewage (9) maintain an equal level.
7. according to right 1 described a kind of ecological blowdown ditch building technology, it is characterized in that: one or more purifying plants (4) in the conventional sewage purification species that purifying plant is selected the collocation humidogene, liked fertile resistant, wastewater purifying efficiency is good or the suitable native country species make up the sewage purification plant community.
8. according to right 1 described a kind of ecological blowdown ditch building technology, it is characterized in that: the option table area is large, and voidage is high, water absorbing properties good, and biological activity is high, chemical composition stability, and nontoxic material is as artificial substratum (3) material.
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Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
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CN110759560A (en) * | 2019-09-30 | 2020-02-07 | 徐顺球 | Multi-layer filtering type sewage treatment device |
Citations (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN2467339Y (en) * | 2001-03-15 | 2001-12-26 | 厉志 | Ornament planting with lawn |
CN1644533A (en) * | 2004-12-29 | 2005-07-27 | 上海交通大学 | Biological adsorbing sightscene floative bed for treating water body as sightscene |
US20060144785A1 (en) * | 2002-05-01 | 2006-07-06 | Edgar Beaulieu | Constructed wetlands system, treatment apparatus and method |
CN201367546Y (en) * | 2009-01-16 | 2009-12-23 | 深圳九华济远环保科技有限公司 | Ecological gutter |
CN101671092A (en) * | 2009-10-12 | 2010-03-17 | 中国农业大学 | Sewage treatment system and method for combined tidal flow artificial wetland |
CN101669434A (en) * | 2009-10-12 | 2010-03-17 | 河北省环境科学研究院 | Suspended rhizoid biological floating bed |
CN201438825U (en) * | 2009-04-21 | 2010-04-21 | 深圳万向泰富环保科技有限公司 | Ecological compound bag for desert afforestation |
CN201567557U (en) * | 2009-11-27 | 2010-09-01 | 北京顺天绿色边坡科技有限公司 | Self-adapting flexible body structure side slop drainage channel |
CN102011379A (en) * | 2010-10-22 | 2011-04-13 | 上海交通大学 | Pollution control method of farmland drainage in plain tidal river network area |
-
2011
- 2011-08-05 CN CN2011102234147A patent/CN102910736A/en active Pending
Patent Citations (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN2467339Y (en) * | 2001-03-15 | 2001-12-26 | 厉志 | Ornament planting with lawn |
US20060144785A1 (en) * | 2002-05-01 | 2006-07-06 | Edgar Beaulieu | Constructed wetlands system, treatment apparatus and method |
CN1644533A (en) * | 2004-12-29 | 2005-07-27 | 上海交通大学 | Biological adsorbing sightscene floative bed for treating water body as sightscene |
CN201367546Y (en) * | 2009-01-16 | 2009-12-23 | 深圳九华济远环保科技有限公司 | Ecological gutter |
CN201438825U (en) * | 2009-04-21 | 2010-04-21 | 深圳万向泰富环保科技有限公司 | Ecological compound bag for desert afforestation |
CN101671092A (en) * | 2009-10-12 | 2010-03-17 | 中国农业大学 | Sewage treatment system and method for combined tidal flow artificial wetland |
CN101669434A (en) * | 2009-10-12 | 2010-03-17 | 河北省环境科学研究院 | Suspended rhizoid biological floating bed |
CN201567557U (en) * | 2009-11-27 | 2010-09-01 | 北京顺天绿色边坡科技有限公司 | Self-adapting flexible body structure side slop drainage channel |
CN102011379A (en) * | 2010-10-22 | 2011-04-13 | 上海交通大学 | Pollution control method of farmland drainage in plain tidal river network area |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN110759560A (en) * | 2019-09-30 | 2020-02-07 | 徐顺球 | Multi-layer filtering type sewage treatment device |
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Application publication date: 20130206 |