CN102190374A - Trickling biofilter - Google Patents
Trickling biofilter Download PDFInfo
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- CN102190374A CN102190374A CN 201110086254 CN201110086254A CN102190374A CN 102190374 A CN102190374 A CN 102190374A CN 201110086254 CN201110086254 CN 201110086254 CN 201110086254 A CN201110086254 A CN 201110086254A CN 102190374 A CN102190374 A CN 102190374A
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- filler module
- bed
- drips
- water
- material filling
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Abstract
The invention relates to a trickling biofilter, which comprises a water inlet pipeline (1), a water distributing system (2), a material filling module (3) and a water outlet system (4). the water inlet pipeline (1) and the water distributing system (2) are provided on the upper of the trickling biofilter, inlet water is uniformly distributed in the material filling module (3), the material filling module (3) is arranged along a vertical direction, the water outlet system (4) is provided at lowest part of the trickling biofilter to collect, backflow and discharge treated water. Compared with the prior art, the material filling module is prepared by a combination of corrugated plate and a connecting rod or one-step injection molding, a gap of the material filling module can be increased, the screened large particle size materials in sewage can be prevented to intercept on a packed bed, sewage is degraded by biochemical action of biomembrane on the surface of the material filling during dropping, shed microbial biofilms can smoothly pass through the grid structure packed bed, clogging of the packed bed can be fundamentally prevented, backwashing can be avoided as well, an operation procedure for treating sewage can be simplified.
Description
Technical field
The present invention relates to technical field of sewage, especially relate to a kind of biology and drip bed.
Background technology
Dirty water living creature processing technique is through 100 years of development, the form that exists of the microorganism that degradation of contaminant is played a major role mainly is divided into two classes, one class is to be discrete type, the flocculu shape of representative with the Activated Sludge Process, and an other class is to be that the microbial film of representative exists form with technologies such as biological filter and blodiscs.Microorganism exists with the microbial film form, can improve waste disposal plant unit volume microorganism concn, thereby effectively increases the treatment unit volumetric loading, improves processing power, strengthens capacity of resisting impact load.
At present, the microbial film sewage disposal technology mainly comprises aerobic contact oxidation, BAF, blodisc and biological filter etc.The microbial film that aerobic contact oxidation (as: number of patent application CN201020237578.6) and BAF (as: patent ZL02129618.9) all are attached to carrier is immersed in the sewage, need to rely on mechanical blast aeration to satisfy the demand of microorganism to oxygen, the energy consumption height, in service can the obstruction needs back flushing.Blodisc technology (as: number of patent application CN201010235846.5), microorganism growth is in the blodisc disc surfaces, rely on the disk body mechanical rotation, microorganism alternately is in the air and sewage in, guaranteed the microorganism oxygen supply, this process machinery equipment complexity, disc surfaces is long-pending little, and processing power is lower.Bio-trickling filter relies on the nature oxygen supply to satisfy the demand of microorganism to oxygen, patent CN200710170419.1 overcomes the treatment effect that exists in the prior art effectively and is subjected to shortcomings such as hydraulic load influences greatly, the easy obstruction in filter tank, but the high-rate filter of the back flushing of exploitation.
Mentioned microorganism is with the sewage treatment process that the microbial film form exists, and the needs that have rely on mechanical blast aeration to satisfy the demand of microorganism to oxygen, the energy consumption height; The mechanical means complexity that has, disc surfaces is long-pending little, and processing power is lower; What have needs back flushing for avoiding stopping up.The existence of this type of problem all impacts sewage treatment process management and energy consumption.
Summary of the invention
Purpose of the present invention be exactly provide a kind of complete modularization in order to overcome the defective that above-mentioned prior art exists, optimized structure, biology easy to use drips bed.
Purpose of the present invention can be achieved through the following technical solutions:
A kind of biology drips bed, it is characterized in that, this biology drips bed and is made of suction culvert, water distribution system, filler module and outlet system, described suction culvert and water distribution system are located at top, and water inlet is evenly distributed in the filler module, and described filler module edge is vertically to setting, top filler module is done support with bottom filler module, need not to be provided with separately bracing frame, described outlet system is located at foot, collection, backflow and emission treatment water.
Described filler module is that rigid plastics, glass reinforced plastic or light-weight metal sheet material are made into grid structure, and this filler module prolongs flow path along vertically corrugated to being designed to.
Described filler module is done support by bottom filler module, need not to be provided with separately bracing frame, the convenient installation.
Described filler module can be combined or single injection-molded by waved plate and union lever, at different concns waste water, select different lengths union lever or waved plate spacing for use, can change filler module gap, preventing in the sewage that big particle diameter material is sized is trapped in bed of packings, sewage relies on the biomembranous biochemical action that the filler top layer adheres to and degrades in the drippage process, the microbial film that comes off can pass the grid structure bed of packings smoothly, fundamentally prevented the bed of packings obstruction, avoid back flushing, simplified sewage disposal operation process.
Described biology drips bed and can design different filler apertures and fill out the water bed height according to flooded condition, owing to need not to be provided with separately bracing frame, only needs the filler module is directly piled up, and can realize biological the building of bed of dripping.Biological dripping between the bed fillers module group controlled appropriate gap, can satisfy the needs of filler top layer microorganism to oxygen by natural oxygen supply.
Compared with prior art, the present invention has the following advantages:
(1) complete modularization from as support, need not support frame or pond body with the filler module, and is simple in structure, and it is convenient to install, and construction investment is economized;
(2) choose suitable filler module aperture, can prevent in the sewage obstruction of the packing layer that the big particle diameter material and the microbial film that comes off cause, avoided back flushing, simplify sewage disposal operation process;
(3) biological dripping between the bed fillers module group controlled appropriate gap, can satisfy the needs of filler top layer microorganism to oxygen by natural oxygen supply, reduces the sewage disposal energy consumption;
(4) optimize the corrugated plate packing surface tissue, make the microbial film of apposition growth have certain thickness, the outer dissolved oxygen concentration of microbial film is high and inboard dissolved oxygen concentration is low, and dissolved oxygen concentration gradient difference has just been created condition for nitrification and denitrification takes place simultaneously.Simultaneously, along the biological bed water (flow) direction of dripping, the distribution difference of dissolved oxygen also for nitrification and denitrification provides condition, has realized simultaneous denitrification.
Can be according to influent quality water yield feature, certain altitude certain volume filler module is handled rank as one, each is handled rank suction culvert, water distribution system and outlet system is set respectively, according to the treatment process requirement, a plurality of processing ranks are passed through series, parallel and mixed running pattern, thereby reach effective processing the sewage of different Pollutant levels;
(5) microorganism exists with the immobilized biomembrane form in the biology bed, and the operational process sludge yield is few, and local anoxic mud is from digestion and metazoan predation, and whole technology excess sludge production is 1/4th of a conventional activated sludge process.
Description of drawings
Fig. 1 drips the two dimensional structure synoptic diagram of bed for this biology;
Fig. 2 is the structural representation of the A-A section among Fig. 1;
Fig. 3 is the structural representation of the B-B section among Fig. 1.
1 is that suction culvert, 2 is that water distribution system, 3 is filler module, 4 outlet systems among the figure.
Embodiment
The present invention is described in detail below in conjunction with the drawings and specific embodiments.
A kind of biology drips bed, its two dimensional structure as shown in Figure 1, this bio-trickling filter is by suction culvert 1, water distribution system 2, filler module 3 and outlet system 4 constitute, suction culvert 1 and water distribution system 2 mainly play the effect that water inlet is evenly distributed to filler module 3, all fillers can both be contacted with sewage, quantity according to flooding quantity and water distribution system 2, on suction culvert 1, offer the hole that diameter is 6mm, making into, water at first is evenly distributed to water distribution system 2 by the pipeline hole, rely on the overflow weir of water distribution system 2 designs to carry out secondary distribution then, water inlet is evenly distributed to filler module 3; Filler module 3 is made by the PVC material, its structure as shown in Figures 2 and 3, in order to increase the path of current through the filler module, filler module 3 edges vertically are designed to wave-like to A-A face and B-B face, when increasing current vertical direction path, current obtain distribution repeatedly under the drainage of filler module 3, make current at whole packing layer uniform distribution, improved effective contact area of the microbial film and the sewage on packing layer surface greatly, strengthened pollutent from sewage to biomembranous mass-transfer efficiency, guaranteed treatment effect, be arranged on top filler module 3 and do support to be arranged on bottom filler module 3, need not to be provided with separately bracing frame, outlet system 5 plays collection, the effect of backflow and emission treatment water, suction culvert 1, water distribution system 2, filler module 3 and outlet system 5 adopt the series operation pattern.
Nothing of the present invention is stopped up, exempt from back flushing, after nature oxygen supply bio-trickling filter microbe inoculation starts, pollutent contained in the water inlet is evenly distributed to filler module 3 with current, fully contact with the microorganism of filling surface apposition growth, mass transfer, under microbial process, be converted into carbonic acid gas and nitrogen etc., realize the degraded of pollutent, at Pollutant levels height or the big water inlet of concentration of suspension, the filler module can be combined or single injection-molded by waved plate and union lever, at different concns waste water, select different lengths union lever or waved plate spacing for use, can change the gap of filler module 3, preventing in the sewage that big particle diameter material is sized is trapped in bed of packings, sewage relies on the biomembranous biochemical action that the filler top layer adheres to and degrades in the drippage process, the microbial film that comes off can pass the grid structure bed of packings smoothly, fundamentally prevent the bed of packings obstruction, avoided back flushing, simplified sewage disposal operation process.The biological bed that drips can design different filler apertures and fill out the water bed height according to flooded condition, owing to need not to be provided with separately bracing frame, only needs the filler module is directly piled up, and can realize biological the building of bed of dripping.Biological dripping between the bed fillers module 3 controlled appropriate gap, can satisfy the needs of filler top layer microorganism to oxygen by natural oxygen supply, can also make the surface-area of unit space filler module 3 big as far as possible, increases bio-trickling filter and handles load.
A kind of biology drips bed, this bio-trickling filter is made of suction culvert, water distribution system, filler module and outlet system, suction culvert and water distribution system mainly play the effect that water inlet is evenly distributed to the filler module, all fillers can both be contacted with sewage, quantity according to flooding quantity and water distribution system, on suction culvert, offer the hole that diameter is 15mm, making into, water at first is evenly distributed to water distribution system by the pipeline hole, rely on the overflow weir of water distribution system design to carry out secondary distribution then, water inlet is evenly distributed to the filler module; The filler module is made by pvc material, in order to increase the path of current through the filler module, with the filler module along vertically to being designed to waviness, when increasing current vertical direction path, current obtain distribution repeatedly under the drainage of filler module, make current at whole packing layer uniform distribution, improved effective contact area of the microbial film and the sewage on packing layer surface greatly, strengthened pollutent from sewage to biomembranous mass-transfer efficiency, guaranteed treatment effect, and top filler module is done support with bottom filler module, need not to be provided with separately bracing frame.Outlet system is located at biological bottom of dripping bed, plays the effect of collection, backflow and emission treatment water, and suction culvert, water distribution system, filler module and outlet system adopt the parallel running pattern.
Claims (5)
1. a biology drips bed, it is characterized in that, this biology drips bed and is made of suction culvert (1), water distribution system (2), filler module (3) and outlet system (4), described suction culvert (1) and water distribution system (2) are located at the top of dripping bed, water inlet is evenly distributed in the filler module (3), described filler module (3) is along vertically to setting, and described outlet system (4) is located at a foot that drips bed, can collect, backflow and emission treatment water.
2. a kind of biology according to claim 1 drips bed, it is characterized in that, described filler module (3) is that rigid plastics, glass reinforced plastic or light-weight metal sheet material are made into this filler module (3) of grid structure along vertically to being designed to bellows-shaped, be arranged on top filler module (3) with the filler module (3) that is arranged on the bottom as support.
3. a kind of biology according to claim 2 drips bed, it is characterized in that, described filler module (3) is the network structure that PVC or polyvinyl chloride light material are made into.
4. a kind of biology according to claim 1 drips bed, it is characterized in that, described filler module (3) is combined or single injection-molded by waved plate and union lever, change union lever length or waved plate spacing to change filler module gap, the filler module (3) that is arranged on top is done support by bottom filler module (3) and directly is piled into the biological bed that drips.
5. a kind of biology according to claim 1 drips bed, it is characterized in that, described suction culvert (1), water distribution system (2), filler module (3) and outlet system (4) can adopt series, parallel or mixed running pattern.
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CN 201110086254 CN102190374B (en) | 2011-04-07 | 2011-04-07 | Trickling biofilter |
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CN102190374B CN102190374B (en) | 2012-12-05 |
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Cited By (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN107824041A (en) * | 2017-12-11 | 2018-03-23 | 黑龙江省能源环境研究院 | A kind of bio-trickling filter of the variable up-hole plate anti-rollover of packing volume |
CN110498568A (en) * | 2019-08-29 | 2019-11-26 | 上海浩为环境工程有限公司 | A kind of sewage simultaneous phosphorus and nitrogen removal integrated apparatus and method |
CN110845005A (en) * | 2019-11-28 | 2020-02-28 | 江南大学 | Method for synchronously desulfurizing and denitrifying wastewater based on biological trickling filter reactor |
CN110950433A (en) * | 2019-11-18 | 2020-04-03 | 深圳市慧创源环保科技有限公司 | Sewage treatment device |
CN110950432A (en) * | 2019-11-18 | 2020-04-03 | 深圳市慧创源环保科技有限公司 | Sewage treatment device |
CN112174336A (en) * | 2020-09-28 | 2021-01-05 | 江苏大学 | Suspended air exposure type biological carrier |
CN112174338A (en) * | 2020-09-28 | 2021-01-05 | 江苏大学 | Suspended air-exposed biological carrier filler |
Families Citing this family (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103304023B (en) * | 2013-05-31 | 2014-11-05 | 浙江省农业科学院 | Powerless-aeration biological filtering bed |
Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1854084A (en) * | 2005-04-28 | 2006-11-01 | 余泰·亚布阿特斯 | Plastic filtering material for wastewater treatment |
CN101045575A (en) * | 2006-03-31 | 2007-10-03 | 邱江平 | Biological weeping pool |
CN101157497A (en) * | 2007-06-29 | 2008-04-09 | 湖南海洁环境技术有限公司 | Dispersed tricking biofilter reactor for treating waste water |
-
2011
- 2011-04-07 CN CN 201110086254 patent/CN102190374B/en active Active
Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1854084A (en) * | 2005-04-28 | 2006-11-01 | 余泰·亚布阿特斯 | Plastic filtering material for wastewater treatment |
CN101045575A (en) * | 2006-03-31 | 2007-10-03 | 邱江平 | Biological weeping pool |
CN101157497A (en) * | 2007-06-29 | 2008-04-09 | 湖南海洁环境技术有限公司 | Dispersed tricking biofilter reactor for treating waste water |
Non-Patent Citations (2)
Title |
---|
《环境污染治理技术与设备》 20040430 张凡等 废水处理用生物填料的研究进展 第8-12页 1-5 第5卷, 第4期 * |
《给水排水》 20011231 王飞际 一种新的污水处理技术-BIOPUR法 第11-14页 1-5 第27卷, 第1期 * |
Cited By (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN107824041A (en) * | 2017-12-11 | 2018-03-23 | 黑龙江省能源环境研究院 | A kind of bio-trickling filter of the variable up-hole plate anti-rollover of packing volume |
CN110498568A (en) * | 2019-08-29 | 2019-11-26 | 上海浩为环境工程有限公司 | A kind of sewage simultaneous phosphorus and nitrogen removal integrated apparatus and method |
CN110950433A (en) * | 2019-11-18 | 2020-04-03 | 深圳市慧创源环保科技有限公司 | Sewage treatment device |
CN110950432A (en) * | 2019-11-18 | 2020-04-03 | 深圳市慧创源环保科技有限公司 | Sewage treatment device |
CN110845005A (en) * | 2019-11-28 | 2020-02-28 | 江南大学 | Method for synchronously desulfurizing and denitrifying wastewater based on biological trickling filter reactor |
CN110845005B (en) * | 2019-11-28 | 2020-12-01 | 江南大学 | Method for synchronously desulfurizing and denitrifying wastewater based on biological trickling filter reactor |
CN112174336A (en) * | 2020-09-28 | 2021-01-05 | 江苏大学 | Suspended air exposure type biological carrier |
CN112174338A (en) * | 2020-09-28 | 2021-01-05 | 江苏大学 | Suspended air-exposed biological carrier filler |
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