Summary of the invention
For the deficiencies in the prior art, the technical problem to be solved in the present invention is to provide the biochemical Sewage treatment systems of integration of a kind of physics and the sewage water treatment method of correspondence thereof.
In order to solve the problems of the technologies described above, the technical solution adopted in the present invention is: a kind of Sewage treatment systems, it comprises collects the water collecting basin that sewage carries out preliminary sedimentation, by the strainer filtering device that input tube is communicated with described water collecting basin, be positioned at the acidification pool in described strainer filtering device downstream, be positioned at the microorganism pond in described acidification pool downstream, be positioned at the micro-pore aeration pond in downstream, described microorganism pond, be positioned at the multifeed clarifier in downstream, described micro-pore aeration pond, be positioned at the sand filter in described multifeed clarifier downstream, layer of sand is provided with bottom described sand filter, described sand filter side is provided with tail vat, offer hole bottom described tail vat stitch with sand filter and pile up sand.
One as the technical scheme of Sewage treatment systems of the present invention is improved, the water level pond receiving settling tank discharge water is provided with between described sand filter and multifeed clarifier, described sand filter is provided with one end and connects the bottom in described water level pond and the strainer tube being connected to the spaced walls in sand filter and water level pond that the other end is closed pluggablely, strainer tube inside is provided with the bag-shaped filter cloth that the filter bowl of tubulose or opening end are fixed on described strainer tube opening part, and the upside of strainer tube is distributed with water vent.
One as the technical scheme of Sewage treatment systems of the present invention is improved, and the rearward end of described strainer tube is overlapped on the future insufficiency place of the corresponding hurdle base of sand filter, and the aft end face of strainer tube is provided with rear footstock.
One as the technical scheme of Sewage treatment systems of the present invention is improved, and the diameter of described water vent is 3-5 millimeter.
One as the technical scheme of Sewage treatment systems of the present invention is improved, described strainer filtering device is comprised the tank be communicated with input tube by water inlet, the side, long limit being positioned at tank the dam lower than other three sides, the filter screen along the downward-sloping setting of dam, is positioned at flow deflector on the downside of filter screen, is provided with supporting clapboard between described filter screen and flow deflector along water (flow) direction.
One as the technical scheme of Sewage treatment systems of the present invention is improved, and described filter screen is S type, the epimere of filter screen be slow down flow velocity heave shape, the hypomere of filter screen is concave shape.
One as the technical scheme of Sewage treatment systems of the present invention is improved, and described filter screen is slope shape and is provided with arc buffering portion at lower slope section.
The method that the present invention carries out sewage disposal is achieved through the following technical solutions, a kind of sewage treatment process using above-mentioned Sewage treatment systems, and it comprises the following steps:
S1, waste water enter water collecting basin, and preliminary sedimentation removes the insoluble substance such as coarse wool bits, hair slag, lime sand grains in water;
S2, waste water enter strainer filtering device through water collecting basin overflow or pump suction, by strainer filtering, suede slag are separated with water;
S3, waste water flow into acidification pool, microorganism pond, micro-pore aeration pond successively, acidification pool and inside, micro-pore aeration pond make it form longer water stream channel by spaced walls, by vertically arranging hairbrush at water stream channel, make the waste water acidifying of sluggish flow, under for the waterplant of biological tank and attached probiotics and secondary bacterium effect thereof, dirt is adsorbed and metabolism purification; Hairbrush in micro-pore aeration pond carries out aeration agitation to waste water, turns out the objectionable impurities in microbial decomposition waste water;
S4, waste water flow into multifeed clarifier, and namely multiple settling tank carries out stationary stream and slowly precipitates;
After S5, multi stage precipitation, overflow forms certain level pressure to water level pond, establishes the strainer tube of filter bowl or filter cloth and then the water vent offered on the upside of strainer tube ejection falls into sand filter in then injecting, and is discharged by sand filter;
The vegetation garden, marsh that the water of S6, discharge drains into side is irrigated, and excessive from the husky wall infiltration of the surrounding underground of a week in vegetation garden, marsh, and then is discharged into the external world;
The mud precipitated in S7, water collecting basin, acidification pool, micro-pore aeration pond, multifeed clarifier is delivered to sludge thickener, and becomes mud cake by sludge dewatering equipment press dewatering.
One as the technical scheme of sewage treatment process of the present invention is improved, and the water that wherein sludge dewatering equipment squeezing is deviate from is drained in microorganism pond.
Beneficial effect of the present invention is: sewage at water collecting basin preliminary sedimentation, filtered coarse sand and part be easy to precipitate impurity, then by strainer filtering device will suspend larger Impurity removal; Then introducing acidification pool makes its acidifying form the environment of applicable microorganism growth; Then the sewage introducing microorganism pond after acidifying is utilized the part objectionable impurities such as grease, ammonia, nitrogen, phosphorus in biological means removal sewage, make chemistry, biochemical oxygen demand (BOD) reaches emission standard; Then enter micro-pore aeration pond to make not remove impurity and form a team further and grow up, then enter multifeed clarifier and precipitate, by under contamination precipitation in stationary stream process, eventually pass husky filter and unprecipitated impurity is stoped among layer of sand, complete sewage disposal.The water quality standard of the tail water obtained can direct reuse in production.
Embodiment
The specific embodiment of the present invention is further illustrated below in conjunction with accompanying drawing.
As Fig. 1, Fig. 3, shown in Fig. 4, a kind of Sewage treatment systems of the present invention, it comprises collects the water collecting basin 11 that sewage carries out preliminary sedimentation, by the strainer filtering device 13 that input tube 12 is communicated with described water collecting basin 11, be positioned at the acidification pool 14 in described strainer filtering device 13 downstream, be positioned at the microorganism pond 15 in described acidification pool 14 downstream, be positioned at the micro-pore aeration pond 16 in downstream, described microorganism pond 15, be positioned at the multifeed clarifier 17 in downstream, described micro-pore aeration pond 16, be positioned at the sand filter 18 in described multifeed clarifier 17 downstream, layer of sand 80 is provided with bottom described sand filter 18, described sand filter 18 side is provided with tail vat 19, offer hole 90 bottom described tail vat 19 with sand filter or stitch and pile up sand.Sewage after water collecting basin 11 carries out preliminary sedimentation, filtered coarse sand and part be easy to precipitate impurity, then by strainer filtering device 13 will suspend larger Impurity removal, as eider down bits; Then put into by sewage and introduce acidification pool 14 and make its acidifying form the environment of applicable microorganism growth, wherein pH value to control between 5.8 to 8.6 and consumes part nutrient, and this nutrient comes from the impurity in sewage; Then the sewage after acidifying is introduced microorganism pond 15 and remove partial impurities with carrying out primary stance environmental protection; Then enter micro-pore aeration pond 16 to make not remove impurity and form a team further and grow up, then enter multifeed clarifier 17 to precipitate, by under contamination precipitation in stationary stream process, eventually pass husky filter and unprecipitated impurity is stoped among layer of sand, complete sewage disposal.The water quality standard of the tail water obtained can direct reuse in production, also can be further purified through biological Swampy Areas and from soil, enter underground, form underground water, realize infiltration type discharge.Therefore sand filter 18 can be filtered the water drainage of oozing out out and biological Swampy Areas are set as its most downstream.
More preferably, simultaneously with reference to shown in figure 2, be provided with the water level pond 79 receiving settling tank discharge water between described sand filter 18 and multifeed clarifier 17, water level pond 79 is flat narrow thus is easy to flood and keeps certain water level, makes it have stable hydraulic pressure.Sand filter 18 is provided with that the bottom in described water level pond 79 is connected in one end and the other end is closed and be connected to the strainer tube 82 of sand filter 18 and the spaced walls in water level pond 79 pluggablely, strainer tube 82 inside is provided with the bag-shaped filter cloth 86 that the filter bowl 85 of tubulose or opening end are fixed on described strainer tube 82 opening part, make strainer tube 82 can carry out follow-up depth type filtration to waste water, the upside of strainer tube 82 is distributed with the water that water vent 88 discharges depth type filtration, and is convenient to from upside ejection the lower inner side that partial impurities is deposited on lateral arrangement body.Strainer tube 82 uses cushion rubber to carry out water-lute with water level pond 79 or multifeed clarifier 17 connection.Filter bowl 85, filter cloth 86 all can take off and clean, and be inserted in strainer tube 82 and continue to use after removing impurity.
More preferably, the rearward end of described strainer tube 82 is overlapped on future insufficiency 83 place of the corresponding hurdle base 81 of sand filter 18, makes strainer tube 82 across the overhead at filtering basin 18, and the water sprayed after filtering falls into sand filter 18 and filters further.The aft end face of strainer tube 82 is provided with rear footstock 89, and the rear end of withstanding strainer tube 82 makes it tightly be plugged on the side of water level pond 79 or multifeed clarifier 17, prevents from leaking.Take off rear footstock 89, then future insufficiency 83 has the overdose space that can retreat for strainer tube 82, is convenient to take off inner filter bowl 85, filter cloth 86 carries out cleaning.In filter cloth 86, bracing frame is set, makes it open and tighten, avoid being close to water vent 88 and prevent filtration area too small.
More preferably, the diameter of described water vent 88 is 3-5 millimeter, is convenient to balance level pressure, prevents pressure from crossing havoc filter bowl filter cloth.
More preferably, simultaneously with reference to shown in figure 5, described strainer filtering device 13 is comprised the tank 33 be communicated with input tube 32 by water inlet 31, the side, long limit being positioned at tank 33 dam 35 lower than other three sides, the filter screen 36 along the downward-sloping setting of dam 35, is positioned at flow deflector 38 on the downside of filter screen 36, by tank 33 and dam 35, moisture stand is flowed down side by side from filter screen 36, under the stop of flow deflector 38, make it flow to next station, and make water flow through certain distance on filtering net, increase filtration area, by current, foreign material can be swept away simultaneously.Supporting clapboard 37 is provided with along water (flow) direction between described filter screen 36 and flow deflector 38, control the current of inside and filter screen 36 better, in filtration procedure, impurity is washed away, impurity on the upside of filter screen 36 brushes down by the excessive anti-rising of inside water pressure, be convenient to the filtration of follow-up impurity, without the need to frequent labor cleaning, reduce labor intensity.
More preferably, described filter screen 36 is S type, the epimere of filter screen be slow down flow velocity heave shape, the hypomere of filter screen 36 is concave shape, makes to be easier to impurity to wash away in heaving of the sea process.
More preferably, described filter screen 36 is slope shape and is provided with arc buffering portion at lower slope section, and impurity is arrived, and lower slope section also can more easily be washed open, prevents from piling up, and manually keeps an eye on without the need to configuring.
The enforcement of above-mentioned Sewage treatment systems, be a kind of sewage treatment process using above-mentioned Sewage treatment systems, it comprises the following steps:
S1, waste water enter water collecting basin 11, and preliminary sedimentation removes the insoluble substance such as coarse wool bits, hair slag, lime sand grains in water; Achieve preliminary filtration, be settled out slightly heavy impurity and insoluble impurities.
S2, waste water enter strainer filtering device 13 through water collecting basin 11 overflow or pump suction, by strainer filtering, suede slag are separated with water; Thus bubble through the water column lighter or suspend and the partial impurities filtering of water quality, as eider down etc.
S3, waste water flow into acidification pool 14, microorganism pond 15, micro-pore aeration pond 16 successively, acidification pool 14 and inside, micro-pore aeration pond 16 make it form longer water stream channel by spaced walls, by vertically arranging hairbrush at water stream channel, make the waste water acidifying of sluggish flow, under for the waterplant of biological tank and attached probiotics and secondary bacterium effect thereof, dirt is adsorbed and metabolism purification; Waste water makes its acidifying form the environment of applicable microorganism growth at acidification pool 14, and wherein pH value to control between 5.8 to 8.6 and consumes part nutrient, and this nutrient comes from the impurity in sewage.Then the sewage after acidifying is introduced microorganism pond 15 and remove partial impurities with carrying out primary stance environmental protection.
Hairbrush in micro-pore aeration pond 16 carries out aeration agitation to waste water, turns out the objectionable impurities in microbial decomposition waste water; Then enter micro-pore aeration pond 16 to make not remove impurity and form a team further and grow up, be convenient to post precipitation and filter.
S4, waste water flow into multifeed clarifier 17, and namely multiple settling tank carries out stationary stream and slowly precipitates; Waste water precipitates at multifeed clarifier 17, by under contamination precipitation in stationary stream process, eventually passes husky filter and is stoped among layer of sand by unprecipitated impurity, complete sewage disposal.
The overflow after multi stage precipitation of S5, waste water forms certain level pressure to water level pond 79, then establish the strainer tube 82 of filter bowl 85 or filter cloth 86 in injecting and the water vent 88 offered on the upside of strainer tube 82 sprays and then falls into sand filter 18, and discharged by sand filter 18; Strainer tube 82 and layer of sand can do further depth type filtration to sewage, and the basic filtering of detrimental impurity, nutritive substance has also been absorbed and used in treating processes.
The vegetation garden, marsh that the water of S6, discharge drains into side is irrigated, and excessive from the husky wall infiltration of the surrounding underground of a week in vegetation garden, marsh, and then is discharged into the external world.The water quality standard of the tail water obtained through sewage treatment step above can direct reuse in production, also can be further purified through biological Swampy Areas and from soil, enter underground, form underground water, realize infiltration type discharge.Therefore sand filter 18 can be filtered the water drainage of oozing out out and biological Swampy Areas are set as its most downstream.
The mud precipitated in S7, water collecting basin, acidification pool, micro-pore aeration pond, multifeed clarifier is delivered to sludge thickener, and becomes mud cake by sludge dewatering equipment press dewatering, and mud cake has many fertilizer nutrients, can the dry rear fertilizer being used as plant growing.
More preferably, the water that wherein sludge dewatering equipment squeezing is deviate from is drained in microorganism pond, and the sewage being about to extruding discharge processes, and avoids sewage directly to put external connection row.
Above disclosedly be only the preferred embodiments of the present invention, certainly can not limit the interest field of the present invention with this, therefore according to the equivalent variations that the present patent application the scope of the claims is done, still belong to the scope that the present invention is contained.