CN107601789A - A kind of integrated form integral life sewage processing method - Google Patents

A kind of integrated form integral life sewage processing method Download PDF

Info

Publication number
CN107601789A
CN107601789A CN201711078167.XA CN201711078167A CN107601789A CN 107601789 A CN107601789 A CN 107601789A CN 201711078167 A CN201711078167 A CN 201711078167A CN 107601789 A CN107601789 A CN 107601789A
Authority
CN
China
Prior art keywords
integrated form
soil
layer
form integral
sewage
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN201711078167.XA
Other languages
Chinese (zh)
Inventor
郭俊元
呼群
戈壁
陈诚
江世林
周禹伶
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
INNER MONGOLIA RIQINGYUAN ENVIRONMENTAL PROTECTION TECHNOLOGY Co Ltd
Chengdu University of Information Technology
Original Assignee
INNER MONGOLIA RIQINGYUAN ENVIRONMENTAL PROTECTION TECHNOLOGY Co Ltd
Chengdu University of Information Technology
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by INNER MONGOLIA RIQINGYUAN ENVIRONMENTAL PROTECTION TECHNOLOGY Co Ltd, Chengdu University of Information Technology filed Critical INNER MONGOLIA RIQINGYUAN ENVIRONMENTAL PROTECTION TECHNOLOGY Co Ltd
Priority to CN201711078167.XA priority Critical patent/CN107601789A/en
Publication of CN107601789A publication Critical patent/CN107601789A/en
Pending legal-status Critical Current

Links

Landscapes

  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
  • Treatment Of Biological Wastes In General (AREA)

Abstract

The invention belongs to sanitary sewage disposal technical field, discloses a kind of integrated form integral life sewage processing method, including:Sanitary sewage enters preparation filter chamber and carries out separation of solid and liquid, into two-stage anaerobic digestion groove;Sanitary sewage is after two-stage anaerobic is handled, into ventilation soil tank, by setting the filler in ventilation soil tank, structure high-performance bio nitrification/denitrifying microorganism environment, the organic matter and ammonia nitrogen in sanitary sewage are removed to greatest extent, and the iron filings laid in filler are changed into Fe through corrosiveness3+, with PO4 3‑Reaction generation precipitation FePO4, and then remove the phosphorus in sanitary sewage.Ventilation soil tank handle water outlet after secondary filter can standard discharge or under ooze.The present invention is integrated form integral life sewage processing method, and construct integrated form integrated equipment for wastewater treatment, without special maintenance, the small-sized sanitary sewage disposal of sanitary sewage and villages and small towns for the vast rural area casual household type in China is a kind of economic and practical sewage treatmentmethod.

Description

A kind of integrated form integral life sewage processing method
Technical field
The invention belongs to sanitary sewage disposal technical field, more particularly to a kind of integrated form integral life sewage processing side Method.
Background technology
The vast people in the countryside in China are sparsely populated, and sanitary sewage amount is small, it is difficult to collect, it is wide to pollute, and treatment effeciency is low, scarce Weary professional and technical personnel.Therefore, distributing domestic sewage in rural areas should be avoided extensive pipeline network construction, subtracted based on treatment in situ Few specialized management safeguards that treatment facility should possess operation management simplicity, energy consumption is low, adapts to impact load, and can be synchronous The features such as organics removal, nitrogen and phosphorous nutrient.At present, domestic sewage in rural areas uses the biologic technology of manual intervention, example more Such as:Anaerobic methane fermentation technique, land treatment technique etc..Anaerobic methane fermentation technique is poor to nitrogen phosphorus ligands effect;Land treatment systems Technology is to carry out integrated treatment, it is necessary to take a large amount of soil to pollutant using the ecosystem of soil, microorganism, plant constitution Ground, underground water pollution is easily caused, and needs periodically harvesting processing growing plants, nitrogen phosphorus ligands effect otherwise can be caused to decline, Soil occurs purification function degeneration because of organic matter accumulation.China " 13 " planning, which proposes, " pushes forward rural residence ring comprehensively The construction object of border regulation, increasing countryside sewage treating ".Therefore, the technology of sustainable, the easy to control nitrogen and phosphorous nutrient of development environment It is most important." around Urban-rural Development integration, going deep into Promoting The Construction of New Countryside " weight proposed according to China " 13 " planning Big historic task, and the construction object of " pushing forward Rural Human Settlements regulation comprehensively, increase countryside sewage treating ", based on current agriculture Village's sanitary sewage disposal technology --- septic tank, stabilization pond, the denitrogenation dephosphorizing present in artificial swamp are difficult, soil organism accumulation With hardened, floor space it is big, recover difficult and the defects of easily cause groundwater environment pollution, devise and a kind of be applied to processing The integrated form integrated treatment unit of rural scattered domestic sewage, to adapt to the vast domestic sewage in rural areas decentralized processing in China Technical requirements.Rural Water Environment problem is serious at present, lacks targetedly advanced and applicable sewage disposal technology.Rural area is dirty at present Method for treating water has:Septic tank, stabilization pond, artificial swamp etc..These technologies are undesirable for the removal efficiency of nitrogen phosphorus, account for simultaneously Ground area is big, and stabilization pond also has serious bed mud mud problem.
In summary, the problem of prior art is present be:At present treatment method for rural sewage exist removal efficiency it is undesirable, Particularly nitrogen phosphorus ligands are poor, while floor space is big, there is serious bed mud mud.
The content of the invention
The problem of existing for prior art, the invention provides a kind of integrated form integral life sewage processing method.
The present invention is achieved in that a kind of integrated form integral life sewage processing method, the integrated form integration Domestic sewage processing method comprises the following steps:
Step 1, sanitary sewage separation of solid and liquid, bulky grain floating object and sediment separation, are removed organic in sanitary sewage Pollutant;
Step 2, the processing of sanitary sewage two-stage anaerobic, ventilation soil tank purify sewage using the effect of soil and microorganism; Biological nitration/denitrifying microorganism environment is built, removes the ammonia nitrogen in sanitary sewage;Iron filings are laid in filler through corrosiveness to turn It is changed into Fe3+, with PO4 3-Reaction generation precipitation FePO4, remove the phosphorus in sanitary sewage;Ventilation soil tank handle standard discharge or under Ooze.
Further, the soil module of the gas permeability soil tank is mixed by pale red earth and sawdust, and loadings are 0.3m3, zeolite filler loadings are 0.5m3, iron filings loadings are 0.03m3;Soil module presses dry weight ratio by pale red earth and sawdust 85:15 are mixed, wherein pale red earth uses the preceding particle that need to be broken for 2~3mm of particle diameter.
Another object of the present invention is to provide a kind of integrated form of the integrated form integral life sewage processing method Integral domestic sewage treatment device, the integrated form integral domestic sewage treatment device include:Preparation filter chamber, one-level are detested Oxygen digestive shelf, secondary anaerobic digestive shelf, ventilation soil tank, secondary filter room, filtering material layer, secondary filter material layer;
Preparation filter chamber is connected by pipeline with one-level anaerobic digestion groove, and one-level anaerobic digestion groove is detested by pipeline and two level Oxygen digestive shelf is connected, and secondary anaerobic digestive shelf is connected by pipeline with ventilation soil tank, and ventilation soil tank passes through pipeline and precision Filter chamber connects.
Further, filtering material layer is uniformly fixed with by bolt in the prepared filter.
Further, the secondary filter room is uniformly fixed with secondary filter material layer by bolt.
Further, the gas permeability soil tank is connected with aeration pump.
Further, the filtering material layer is special layer of cloth, lays 20 layers, thickness 10mm, interlamellar spacing 50mm.
Further, aeration tubular type biogas stirring device is set in the one-level anaerobic digestion groove, secondary anaerobic digestive shelf is not set Biogas stirring device.
Further, the gas permeability soil tank is bio-trickling filter structure, structure in the reactor of the gas permeability soil tank Soil module, zeolite filter layer, iron filings layer alternatively layered arrangement are built;
Soil module, zeolite filter layer, iron filings layer alternatively layered arrangement, gas permeability soil pot bottom filling boulder bed, and Upstream sequence alternately fills zeolite layer, iron filings layer, soil module layer successively afterwards;Boulder bed, zeolite layer, iron filings layer, soil module The number of plies is respectively 1~2 layer, 3~5 layers, 2~4 layers, 2~4 layers.
Further, the secondary filter room, which integrates, hides water tank, collector pipe, the device of sprinkler, the collector pipe, dissipates Hydrophone, which is laid on, to be hidden inside water tank;The sprinkler is laid on collector pipe top;The sprinkler is equipped with multilayer layer of cloth, layer Thick 10mm, interlamellar spacing 50mm.
Advantages of the present invention and good effect are:Septic tank, artificial swamp, the treatment technology such as stabilization pond used with tradition Compare, pave iron filings thin layer in gas permeability soil tank, and fills zeolite filler layer, can realize organic contamination in sanitary sewage The synchronous removal of thing, nitrogen phosphorus;The maximum mechanical aeration system construction of energy consumption is avoided, floor space is saved, has saved largely Maintenance cost.Central No. 1 files in 2011 and central water conservancy working conference, which are distinctly claimed, carries out most stringent water resources managing system Degree, receive dirty red line wherein having and establishing Water Functional Zone limitation, enter the overall control of river lake in Water Functional Zone to the year two thousand thirty major pollutants Within the scope of pollutant carrying capacity, Water Functional Zone probability of meeting water quality standard brings up to more than 95% requirement, integrated form of the invention integration Sewage treatment unit has adapted to the requirement of national relevant policies completely.
Rural Water Environment problem is serious at present, lacks targetedly advanced and applicable sewage disposal technology.Rural area is dirty at present Method for treating water has:Septic tank, stabilization pond, artificial swamp etc..These technologies are undesirable for the removal efficiency of nitrogen phosphorus, account for simultaneously Ground area is big, and stabilization pond also has serious bed mud mud problem.This integrated form integral domestic sewage treatment device is built It is low with operating cost, ingenious in design, simple in construction, good denitrogenation and dephosphorization effect and stably (including COD, ammonia nitrogen, TN, TP are gone Except).Local resources can be made full use of simultaneously, different fillers are added to the dirty removal capacities that mixed model layer carrys out strengthening system. Handle water can with reuse, system can with longtime running, it is retired after filler can reclaim and returns farmland to use, improve resource reusing rate. In villages and small towns, sewage treatment area has higher promotional value, is suitable for the more backward rural area of economy and disperses at the sewage such as peasant household Reason.The present invention constructs corresponding integrated form integrated equipment for wastewater treatment by integrated form integral life sewage processing method, It is one for the small-sized sanitary sewage disposal of sanitary sewage and villages and small towns of the vast rural area casual household type in China without special maintenance The economic and practical sewage treatmentmethod of kind.
Using hydraulic load as 400L/ (m2D) exemplified by, after treatment, COD, ammonia nitrogen, total nitrogen, total phosphorus in sanitary sewage Clearance be respectively 93.4%, 94.9%, 80.4%, 94.7%, processing effluent quality meet urban wastewater treatment firm pollute Thing discharge standard (GB18918-2002) first discharge standard A requirements.And COD 215mg/L, ammonia nitrogen in undressed raw water 45mg/L, total nitrogen 60mg/L, total phosphorus 5mg/L.The annual waste water total release in China reaches up to 600 billion cubic meters, wherein small towns sewage 200 billion cubic meters, domestic sewage in rural areas is up to 80 billion cubic meters, and there are 600,000 administrative villages in China, more than 250 ten thousand natural villages, wherein 96% village does not have discharge conduit and sewage disposal system, and sanitary sewage arbitrarily discharges.From this view, annual emission reduction About 1,200,000 tons respectively, 260,000 tons, 300,000 tons, 30,000 tons of COD, ammonia nitrogen, total nitrogen, total phosphorus.
Brief description of the drawings
Fig. 1 is integrated form integral life sewage process flow figure provided in an embodiment of the present invention;
Fig. 2 is integrated form integral domestic sewage treatment device structural representation provided in an embodiment of the present invention;
In figure:1st, preparation filter chamber;2nd, one-level anaerobic digestion groove;3rd, secondary anaerobic digestive shelf;4th, ventilation soil tank;5th, it is smart Close filter chamber;6th, filtering material layer;7th, secondary filter material layer.
Embodiment
In order to make the purpose , technical scheme and advantage of the present invention be clearer, with reference to embodiments, to the present invention It is further elaborated.It should be appreciated that the specific embodiments described herein are merely illustrative of the present invention, it is not used to Limit the present invention.
The application principle of the present invention is explained in detail below in conjunction with the accompanying drawings.
As shown in figure 1, integrated form integral life sewage processing method provided in an embodiment of the present invention comprises the following steps:
S101:Sanitary sewage initially enters prepared filter chamber and carries out separation of solid and liquid, by the floating object and sediment of bulky grain After separating, into two-stage anaerobic digestion groove, the organic pollution in sanitary sewage is removed to greatest extent;
S102:Sanitary sewage is after two-stage anaerobic is handled, and into ventilation soil tank, ventilation soil tank mainly utilizes soil The effect purification sewage of earth and microorganism, by setting the filler in ventilation soil tank, it is configured to high-performance bio nitrification/anti- Nitrifying microorganisms environment, the ammonia nitrogen in sanitary sewage can be removed to greatest extent, the iron filings laid in filler are through corrosiveness It is changed into Fe3+, easily and PO4 3-Reaction generation precipitation FePO4, and then the phosphorus in sanitary sewage is removed, the processing water outlet of ventilation soil tank After secondary filter can standard discharge or under ooze.
As shown in Fig. 2 integrated form integral domestic sewage treatment device provided in an embodiment of the present invention includes:Preparation filtering Room 1, one-level anaerobic digestion groove 2, secondary anaerobic digestive shelf 3, ventilation soil tank 4, secondary filter room 5, filtering material layer 6, precision Filtering material layer 7.
Preparation filter chamber 1 is connected by pipeline with one-level anaerobic digestion groove 2, and one-level anaerobic digestion groove 2 passes through pipeline and two Level anaerobic digestion groove 3 is connected, and secondary anaerobic digestive shelf 3 is connected by pipeline with ventilation soil tank 4, and ventilation soil tank 4 passes through pipe Road is connected with secondary filter room 5, is uniformly fixed with filtering material layer 6 in preparation filter 1 by bolt, and secondary filter room 5 is logical Cross bolt and be uniformly fixed with secondary filter material layer 7.Gas permeability soil tank 4 is connected with aeration pump.
The integrated form integral life sewage processing method set provided in an embodiment of the present invention core of sewage treatment process Heart function, including pretreatment, biological treatment/biochemical treatment;Corresponding integrated form integrated equipment for wastewater treatment is by preparing filter chamber, one Level anaerobic digestion groove, secondary anaerobic digestive shelf, ventilation soil tank, secondary filter room composition.Sanitary sewage, which initially enters, to be prepared Filter chamber carries out separation of solid and liquid, after the floating object of bulky grain and sediment are separated, into two-stage anaerobic digestion groove, maximum limit Degree ground removes the organic pollution in sanitary sewage;Sanitary sewage, into ventilation soil tank, is breathed freely after two-stage anaerobic is handled Soil tank is mainly the effect purification sewage using soil and microorganism, by setting the filler in ventilation soil tank, by its structure Build as high-performance bio nitrification/denitrifying microorganism environment, the ammonia nitrogen in sanitary sewage, filler middle berth can be removed to greatest extent If iron filings be changed into Fe through corrosiveness3+, easily and PO4 3-Reaction generation precipitation FePO4, and then the phosphorus in sanitary sewage is removed, Ventilation soil tank handle water outlet after secondary filter can standard discharge or under ooze.
For preparation filter chamber:The spy of the present invention is used to weave cotton cloth as filtering material.
For two-stage anaerobic digestion groove:Wherein first order anaerobic digestion groove inside sets agitating device using digesting at a high speed, can Shorten organic pollution and stablize the required time, remove the organic pollution in sanitary sewage, second level anaerobism to greatest extent Digestive shelf does not set stirring, primarily serves precipitation concentration and stores the effect of decomposed sludge, and separates and exclude supernatant.
It is mainly anaerobism microenvironment in the case of artificial intermittent aeration, in soil module layer, in zeolite filter layer and iron filings layer Predominantly aerobic microenvironment, gas permeability soil tank are horizontal-flow type, and intermittent water inflow, when sanitary sewage flows through, ammonia nitrogen is easily by zeolite Absorption, will there is nitrobacteria growth in aerobic microenvironment, and the partial organic substances in sewage are then in the form of carbon source by heterotrophism Bacterium is utilized, and the nitrate nitrogen that ammonia nitrogen changes into through nitrifier then removes in anaerobic environment through denitrification, organic in sewage Sawdust in thing and soil module can be used as denitrifying carbon source, the presence of multiple Aerobic-anaerobic microenvironments in gas permeability soil tank, Help to weaken nitrifier and competition and denitrifying bacterium and other heterotrophs competition to organic carbon source of the heterotroph to oxygen, have Beneficial to the completion of whole biological nitrification and denitrification process, fe is changed into Fe through corrosiveness3+, easily and PO4 3-Reaction generation is heavy Shallow lake FePO4, and then be removed.
For secondary filter room:By the collection secondary filter Jing Guo particular design such as screening water tank, collector pipe, aproll equipment and dissipate Drainage facility is in the special device of one.
The application principle of the present invention is further described with reference to specific embodiment.
Embodiment 1:
Simulated domestic wastewater water quality:COD 215mg/L, ammonia nitrogen 45mg/L, total nitrogen 60mg/L, total phosphorus 5mg/L, sewage pH are 6.5。
(1) the biofilm stage:
Water inlet hydraulic load is set as 200L/ (m2D), after startup optimization 28d, COD, ammonia nitrogen, TN, TP in water outlet are handled Clearance respectively reaches 84.5%, 75.1%, 68.1%, 78.4%, hereafter week age, handle water outlet in COD, ammonia nitrogen, The relative deviation of the adjacent monitoring result twice of TN, TP is below 5%, illustrates to have reached stable running status.
(2) the sanitary sewage disposal stage:
1. the removal of organic pollution in pair sanitary sewage:Intake hydraulic load respectively 300,400,500L/ (m2·d) Under conditions of, the average removal rate for handling COD in water outlet is above 83.3%, and processing effluent COD concentration is below 50mg/L, full The A standards of sufficient urban wastewater treatment firm pollutant emission standard (GB18918-2002) first discharge standard.Pass through law of conservation It was found that contribution contribution rate of the microorganism to organic matter removal is respectively 54.3%, 72.1%, 66.1%, the contribution of filling adsorption Rate is respectively 30.8%, 21.3%, 17.2%.
The removal of 2 pairs of Ammonia Nitrogen in Municipal Wastewater:Intake hydraulic load respectively 300,400,500L/ (m2D) condition Under, for ammonia nitrogen removal frank more than 88.8%, processing water outlet ammonia nitrogen concentration is below 5mg/L, meets urban wastewater treatment firm dirt Contaminate the A standards of thing discharge standard (GB18918-2002) first discharge standard.Found by law of conservation, microorganism goes to ammonia nitrogen The contribution contribution rate removed is respectively 53.8%, 68.7%, 55.8%, the contribution rate of filling adsorption is respectively 34.3%, 26.2%, 19.8%.In addition, 400L/ (m2D) under the conditions of hydraulic load, gas permeability soil tank is to ammonia nitrogen removal speed and nitrate nitrogen output speed Rate is stablized in 17.5g NH respectively+ 4-N/(m2And 6.6g NO d)- 3-N/(m2·d)。
3. TN removal in pair sanitary sewage:Hydraulic load intake respectively in 300,400L/ (m2D) under conditions of, place The clearance of TN in water outlet is managed more than 76.0%, water outlet TN mean concentrations are less than 15mg/L, meet urban wastewater treatment firm dirt Contaminate the A standards of thing discharge standard (GB18918-2002) first discharge standard.Found by law of conservation, microorganism removes to TN Contribution contribution rate be respectively 43.7%, 55.9%, the contribution rate of filling adsorption is respectively 32.3%, 24.5%.
4. TP removal in pair sanitary sewage:Intake hydraulic load respectively 300,400,500L/ (m2D) condition Under, the level that TP concentration in water outlet is maintained at a below 0.5mg/L all the time is handled, meets urban wastewater treatment firm pollutant emission mark The A standards of accurate (GB18918-2002) first discharge standard.Found by law of conservation, the contribution contribution that microorganism removes to TP Rate is respectively 21.6%, 24.3%, 21.8%, and the contribution rate of filling adsorption is respectively 71.5%, 70.4%, 72.3%.
(3) the biofilm stage, more bacteriums in biomembrane, protozoan and metazoa are less, a large amount of paramecium can be observed; Stable operation stage, it is attached to and occurs the largely infusorian using organic matter as food in the biomembrane of zeolite filler, can also see Campanularian, tired branch worm etc. are observed, is attached in the biomembrane of soil module and is interspersed with der Pilz and wheel animalcule, paramecium quantity subtracts greatly, Further illustrate that the integrated form integrated technique of this research and establishment has preferable processing to sanitary sewage in terms of microbial Effect.
In a word, hydraulic load is 400L/ (m2When d), COD, ammonia nitrogen, TN, TP average removal rate point in sanitary sewage Not Wei 93.4%, 94.9%, 80.4%, 94.7%, processing effluent quality meet urban wastewater treatment firm pollutant emission standard (GB18918-2002) first discharge standard A requirements.
Embodiment 2
1st, domestic sewage in rural areas, specification of works 1t/d;
Core process:Preparation filter chamber → two-stage anaerobic digestion groove → gas permeability soil tank → secondary filter → sterilization → up to standard Discharge.
2nd, primary operating parameter:
Hydraulic load:200-400L/(m2·d);
Hydraulic detention time:24-48h.
3rd, key equipment and device parameter:
Preparation filter chamber:Filtering material is the special cloth of autonomous Design, lays 20 layers, thickness 10mm, interlamellar spacing 50mm;
Anaerobic digestion groove:The high speed digestive shelf of autonomous Design, inside sets stirring, is stirred using aeration tubular type (gas formula) biogas Mix, caliber 20mm, Chi Gai, the insulation material of pool wall use polyurethane rigid foam plastic, and thickness is 20mm.
Gas permeability soil tank:Reactor is designed as bio-trickling filter structure, percent opening 30%, and level stream mode is run, instead Structure soil module, zeolite filter layer, iron filings layer in device are answered, soil module is by pale red earth and sawdust by certain dry weight ratio mixing system Into loadings 0.3m3, zeolite filler loadings are 0.5m3, iron filings loadings are 0.03m3.Soil module, zeolite filter layer, Iron filings layer requires to carry out alternatively layered arrangement according to gas permeability soil tank.For ventilation soil tank:Soil is built in soil tank Module, zeolite filter layer, iron filings layer, soil module press dry weight ratio 85 by pale red earth and sawdust:15 are mixed, zeolite filter layer Using natural clinoptilolite;Iron filings are from machining factories such as lathes.Gas permeability soil pot bottom first fill boulder bed 50~ 150, then upstream sequence replaces successively fills zeolite layer (50~70mm of floor height), iron filings layer (8~12mm of floor height), soil module Layer (70~90mm of floor height), boulder bed, zeolite layer, iron filings layer, the soil module number of plies are respectively 1~2 layer, 3~5 layers, 2~4 layers, 2~4 layers.Used 3~5mm of sized zeolite particles, for the clinoptilolite from Jinyun county, Zhejiang province;Soil module is pressed by pale red earth and sawdust Dry weight is than 85:15 are mixed, wherein pale red earth uses the preceding particle that need to be broken for particle diameter about 2~3mm.
Secondary filter room:Integrating for autonomous Design hides water tank, collector pipe, the special device of aproll equipment, hides water tank Specification 1.2m × 0.8m × 1m, catchment caliber 20mm, and aproll equipment is the special cloth of autonomous Design, lays 20 layers, thickness 10mm, Interlamellar spacing 50mm.
4th, sewage disposal terminal effluent quality is as follows:
COD (COD, mg/L):35
Biochemical oxygen demand (BOD) (BOD5, mg/L):8
PH value (dimensionless):6.5-6.7
Ammonia nitrogen (mg/L):3.62
TP(mg/L):0.38
TN(mg/L):9.37
SS(mg/L):4.6
5th, effluent quality meets that urban wastewater treatment firm pollutant emission standard (GB18918-2002) first grade discharging A is marked It is accurate.
6th, investment and operating cost:
The integrated form integral domestic sewage treatment device of embodiment 2 uses steel construction, 15000 yuan of buying steel expense.
Equipment and materials:1,500 yuan, immersible pump;Pipeline and water-locator, 500 yuan;Zeolite, according to gas permeability soil tank cloth Put, need 0.5m altogether3, 500 yuan/ton of the market price, zeolite density 2.0g/cm3, then 500 yuan of zeolite expense;Iron filings, according to gas permeability Soil tank is arranged, needs 0.03m altogether3, the density 7.85g/cm of iron3, in actual applications, using waste and old iron wire, iron sheet, machining Caused scum chip etc., according to the 0.6 yuan/kg of scrap iron unit take-back cost in 2016, then cost with 142 yuan, altogether 500+500+500 + 142=1642 members.
Equipment uses buried installation, builds installation fee:3000 yuan.
In this way, for single user, construction project, which takes, to be added up to about:
15000+1642+3000=19642 members.
Operation is taken to be limited in year 15 years, then yearly depreciation charge is 1310 yuan.
Compare the domestic sewage of villages and small towns centralized collection of concentration if considering to live, unified to build, then the construction investment will be by Significantly lower in scale effect.
With reference to practical operation situation, water pump adds up operation 0.4h daily, power 0.2kW, efficiency 0.55, and 0.6 yuan of electricity price/ KWh is counted, then daily operating cost:
E=(0.2 × 0.4 × 0.6)/0.55=0.09 members.
For single household resident, the actual electricity charge daily are 0.09 yuan.
For the rural households of 5 people, the system is often only in use to be needed:
1310+0.09 × 1343 yuan of 365 ≈, wherein containing capital cost and operating cost.
Stabilization pond with easily tens up to a million yuan, compared with the capital cost of artificial swamp, cost is at a fairly low.
7th, the energy, resources conservation and comprehensive utilization situation:
1) construction of the mechanical aeration system that energy consumption is maximum in the aerobic sewage disposal technology of tradition is avoided, builds and runs Cost is low;
2) degraded to organic matter can be efficiently accomplished, and being capable of synchronous denitrification dephosphorizing;
3) it is simple in construction, it is quick for installation, it is simple to operate, it is easily managed, it is not necessary to extra ventilation aeration, nothing after successful operation Professional and technical personnel is needed to safeguard, floor space is small, and the power consumption of water pump is removed after operation, and other almost do not have operating cost, It is energy-saving compared to legacy equipment obvious;
4) using the present invention because its good denitrogenation and dephosphorization effect, water outlet of the present invention are applied primarily in agricultural irrigation, Ji Nengbao Demonstrate,prove the hygienic quality of crops, ensure the quality of soil, also can guarantee that the quality of underground water is not affected.
The foregoing is merely illustrative of the preferred embodiments of the present invention, is not intended to limit the invention, all essences in the present invention All any modification, equivalent and improvement made within refreshing and principle etc., should be included in the scope of the protection.

Claims (10)

1. a kind of integrated form integral life sewage processing method, it is characterised in that at the integrated form integral life sewage Reason method comprises the following steps:
Step 1, sanitary sewage separation of solid and liquid, bulky grain floating object and sediment separation, remove the organic contamination in sanitary sewage Thing;
Step 2, the processing of sanitary sewage two-stage anaerobic, ventilation soil tank purify sewage using the effect of soil and microorganism;Structure Biological nitration/denitrifying microorganism environment, remove the ammonia nitrogen in sanitary sewage;Iron filings are laid in filler through corrosiveness to be changed into Fe3+, with PO4 3-Reaction generation precipitation FePO4, remove the phosphorus in sanitary sewage;Ventilation soil tank handle standard discharge or under ooze.
2. integrated form integral life sewage processing method as claimed in claim 1, it is characterised in that the gas permeability soil The soil module of tank is mixed by pale red earth and sawdust, loadings 0.3m3, zeolite filler loadings are 0.5m3, iron filings dress The amount of filling out is 0.03m3;Soil module presses dry weight ratio 85 by pale red earth and sawdust:15 are mixed, wherein pale red earth is using preceding needing brokenly The broken particle for 2~3mm of particle diameter.
3. at a kind of integrated form integral life sewage of integrated form integral life sewage processing method as claimed in claim 1 Manage device, it is characterised in that the integrated form integral domestic sewage treatment device includes:Preparation filter chamber, one-level anaerobism disappear Change groove, secondary anaerobic digestive shelf, ventilation soil tank, secondary filter room, filtering material layer, secondary filter material layer;
Preparation filter chamber is connected by pipeline with one-level anaerobic digestion groove, and one-level anaerobic digestion groove is disappeared by pipeline and secondary anaerobic Change groove connection, secondary anaerobic digestive shelf is connected by pipeline with ventilation soil tank, and ventilation soil tank passes through pipeline and secondary filter Room connects.
4. integrated form integral domestic sewage treatment device as claimed in claim 3, it is characterised in that the prepared filter It is interior that filtering material layer is uniformly fixed with by bolt.
5. integrated form integral domestic sewage treatment device as claimed in claim 3, it is characterised in that the secondary filter room Secondary filter material layer is uniformly fixed with by bolt.
6. integrated form integral domestic sewage treatment device as claimed in claim 3, it is characterised in that the gas permeability soil Tank is connected with aeration pump.
7. integrated form integral domestic sewage treatment device as claimed in claim 3, it is characterised in that the filtering material layer For special layer of cloth, 20 layers, thickness 10mm, interlamellar spacing 50mm are laid.
8. integrated form integral domestic sewage treatment device as claimed in claim 3, it is characterised in that the one-level anaerobism disappears Aeration tubular type biogas stirring device is set in change groove, secondary anaerobic digestive shelf does not set biogas stirring device.
9. integrated form integral domestic sewage treatment device as claimed in claim 3, it is characterised in that the gas permeability soil Tank is bio-trickling filter structure, and soil module, zeolite filter layer, iron filings layer are constructed in the reactor of the gas permeability soil tank Alternatively layered is arranged;
Soil module, zeolite filter layer, iron filings layer alternatively layered arrangement, gas permeability soil pot bottom filling boulder bed, and it is backward Upper order alternately fills zeolite layer, iron filings layer, soil module layer successively;Boulder bed, zeolite layer, iron filings layer, the soil module number of plies Respectively 1~2 layer, 3~5 layers, 2~4 layers, 2~4 layers.
10. integrated form integral domestic sewage treatment device as claimed in claim 3, it is characterised in that the secondary filter Room, which integrates, hides water tank, collector pipe, the device of sprinkler, and the collector pipe, sprinkler, which are laid on, to be hidden inside water tank;It is described Sprinkler is laid on collector pipe top;The sprinkler is equipped with multilayer layer of cloth, thickness 10mm, interlamellar spacing 50mm.
CN201711078167.XA 2017-11-06 2017-11-06 A kind of integrated form integral life sewage processing method Pending CN107601789A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201711078167.XA CN107601789A (en) 2017-11-06 2017-11-06 A kind of integrated form integral life sewage processing method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201711078167.XA CN107601789A (en) 2017-11-06 2017-11-06 A kind of integrated form integral life sewage processing method

Publications (1)

Publication Number Publication Date
CN107601789A true CN107601789A (en) 2018-01-19

Family

ID=61085014

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201711078167.XA Pending CN107601789A (en) 2017-11-06 2017-11-06 A kind of integrated form integral life sewage processing method

Country Status (1)

Country Link
CN (1) CN107601789A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111302563A (en) * 2020-02-21 2020-06-19 宁夏水投环保发展有限公司 Widely applicable and selective landfill leachate treatment process and method

Citations (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
AU8611198A (en) * 1998-01-27 1999-01-07 Peter Harte Waste treatment system and method
CA2279525A1 (en) * 1999-08-03 2001-02-03 Institut National De La Recherche Scientifique Hybrid biological and chemical process for decontaminating municipal sewage sludge
CN1709810A (en) * 2005-05-27 2005-12-21 湖北大学 Domestic sewage denitrifying-dephosphorizing method and apparatus
CN1803671A (en) * 2006-01-24 2006-07-19 北京工业大学 Optimized control method of anaerobic-anoxic-aerobic process denitrifying phosphorus removal
CN201109747Y (en) * 2007-07-19 2008-09-03 张富年 Anaerobic-aerobic treatment system apparatus for countryside domesticity sewage
CN102145968A (en) * 2011-05-17 2011-08-10 浙江省环境保护科学设计研究院 Rural domestic sewage treatment process
CN102295388A (en) * 2011-07-28 2011-12-28 农业部规划设计研究院 Filter tank-soil groove ecological treating system and process for rural domestic sewage
CN103030251A (en) * 2012-12-31 2013-04-10 浙江工商大学 Two-phase layered domestic sewage percolation treatment system
CN104058556A (en) * 2014-07-08 2014-09-24 湖南大学 Sewage treatment system employing vertical flow biological trickling and horizontal flow multi-medium soil infiltration
CN104556391A (en) * 2014-12-31 2015-04-29 东莞市蓝天创达化工有限公司 Artificial wetland purification method for wastewater
CN106430541A (en) * 2016-09-26 2017-02-22 成都信息工程大学 Biological trickling filter treatment system and treatment method of domestic wastewater
CN207659265U (en) * 2017-11-06 2018-07-27 成都信息工程大学 A kind of integrated form integral domestic sewage treatment device

Patent Citations (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
AU8611198A (en) * 1998-01-27 1999-01-07 Peter Harte Waste treatment system and method
CA2279525A1 (en) * 1999-08-03 2001-02-03 Institut National De La Recherche Scientifique Hybrid biological and chemical process for decontaminating municipal sewage sludge
CN1709810A (en) * 2005-05-27 2005-12-21 湖北大学 Domestic sewage denitrifying-dephosphorizing method and apparatus
CN1803671A (en) * 2006-01-24 2006-07-19 北京工业大学 Optimized control method of anaerobic-anoxic-aerobic process denitrifying phosphorus removal
CN201109747Y (en) * 2007-07-19 2008-09-03 张富年 Anaerobic-aerobic treatment system apparatus for countryside domesticity sewage
CN102145968A (en) * 2011-05-17 2011-08-10 浙江省环境保护科学设计研究院 Rural domestic sewage treatment process
CN102295388A (en) * 2011-07-28 2011-12-28 农业部规划设计研究院 Filter tank-soil groove ecological treating system and process for rural domestic sewage
CN103030251A (en) * 2012-12-31 2013-04-10 浙江工商大学 Two-phase layered domestic sewage percolation treatment system
CN104058556A (en) * 2014-07-08 2014-09-24 湖南大学 Sewage treatment system employing vertical flow biological trickling and horizontal flow multi-medium soil infiltration
CN104556391A (en) * 2014-12-31 2015-04-29 东莞市蓝天创达化工有限公司 Artificial wetland purification method for wastewater
CN106430541A (en) * 2016-09-26 2017-02-22 成都信息工程大学 Biological trickling filter treatment system and treatment method of domestic wastewater
CN207659265U (en) * 2017-11-06 2018-07-27 成都信息工程大学 A kind of integrated form integral domestic sewage treatment device

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
杨福玲;李玲杉;: "乡镇污水处理技术探讨" *

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111302563A (en) * 2020-02-21 2020-06-19 宁夏水投环保发展有限公司 Widely applicable and selective landfill leachate treatment process and method

Similar Documents

Publication Publication Date Title
CN204125300U (en) A kind of purification tank for the treatment of dispersion type domestic wastewater
CN102775025B (en) Municipal life wastewater treatment system with high efficiency and low energy consumption
CN102491594B (en) Multifunctional stereo comprehensive treatment and recycling system for urban sewage
CN101973679B (en) Distributed sewage treatment and regeneration technology
CN105461165A (en) Rural domestic sewage combined type ecological treatment system and treatment method, and application thereof
CN110040916A (en) A kind of complete processing system and its processing method of black and odorous water
CN101585607B (en) Preparation method for substrate of vertical-flow constructed wetlands
Li et al. Distributed treatment of rural environmental wastewater by artificial ecological geographic information system
CN205398371U (en) Rural miniaturized integration sewage treatment unit
CN203269716U (en) Artificial rapid infiltration system for industrial park sewage treatment
CN109111050A (en) Solar energy microkinetic rural sewage treatment system
CN102040316B (en) Method for purifying ecological compound sludge water body
CN109320012B (en) Municipal sewage treatment system and method
CN106430541A (en) Biological trickling filter treatment system and treatment method of domestic wastewater
CN103739172B (en) Water circulating and reusing method for industrial parks
CN205295076U (en) Environmental sewage treatment system device of service area based on bological aerated filter
CN207659265U (en) A kind of integrated form integral domestic sewage treatment device
Xia et al. The advanced nutrient removal efficiency and microbial community of a pipeline biofilm system for tailwater transportation
CN103159379A (en) System and method for treating sewage at zero energy consumption by using ecological filter bed
CN107601789A (en) A kind of integrated form integral life sewage processing method
CN110171903A (en) City micropolluted river water processing method and system
CN102372394A (en) Method for treating rural sewage with effect of removing phosphate and nitrogen
CN105130124B (en) The collaboration minimizing technology of nitrate nitrogen, ammonia nitrogen and COD in a kind of polluted-water
CN101607775A (en) Earthworm and ecological filter-denitrification bio-filter combined system is handled organic sewage technology
CN211644786U (en) Biochemical wetland ecological purification system for new rural domestic sewage

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination