CN201406359Y - Treatment device for black and odorous river course - Google Patents
Treatment device for black and odorous river course Download PDFInfo
- Publication number
- CN201406359Y CN201406359Y CN2009200699858U CN200920069985U CN201406359Y CN 201406359 Y CN201406359 Y CN 201406359Y CN 2009200699858 U CN2009200699858 U CN 2009200699858U CN 200920069985 U CN200920069985 U CN 200920069985U CN 201406359 Y CN201406359 Y CN 201406359Y
- Authority
- CN
- China
- Prior art keywords
- river course
- floating bed
- controlling device
- black smelly
- water
- 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.)
- Expired - Fee Related
Links
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 71
- 238000005192 partition Methods 0.000 claims abstract description 26
- 230000007246 mechanism Effects 0.000 claims abstract description 9
- 238000011144 upstream manufacturing Methods 0.000 claims abstract description 6
- 238000005276 aerator Methods 0.000 claims description 7
- 239000004746 geotextile Substances 0.000 claims description 7
- 230000003139 buffering effect Effects 0.000 claims 8
- 230000001706 oxygenating effect Effects 0.000 claims 3
- 239000002054 inoculum Substances 0.000 claims 1
- 230000000694 effects Effects 0.000 abstract description 12
- 238000005273 aeration Methods 0.000 abstract description 8
- 239000005416 organic matter Substances 0.000 abstract description 8
- 238000000746 purification Methods 0.000 abstract description 6
- 241000196324 Embryophyta Species 0.000 description 11
- 239000000945 filler Substances 0.000 description 11
- 244000005700 microbiome Species 0.000 description 11
- 238000011065 in-situ storage Methods 0.000 description 8
- 239000003344 environmental pollutant Substances 0.000 description 7
- 231100000719 pollutant Toxicity 0.000 description 7
- 238000010586 diagram Methods 0.000 description 5
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 4
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 4
- 230000033558 biomineral tissue development Effects 0.000 description 4
- 238000006213 oxygenation reaction Methods 0.000 description 4
- 239000002689 soil Substances 0.000 description 4
- 230000009471 action Effects 0.000 description 3
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 3
- 238000000034 method Methods 0.000 description 3
- 235000015097 nutrients Nutrition 0.000 description 3
- 229910052760 oxygen Inorganic materials 0.000 description 3
- 239000001301 oxygen Substances 0.000 description 3
- 239000002245 particle Substances 0.000 description 3
- 239000010865 sewage Substances 0.000 description 3
- 230000009466 transformation Effects 0.000 description 3
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 2
- 229910000831 Steel Inorganic materials 0.000 description 2
- 230000009286 beneficial effect Effects 0.000 description 2
- 230000015556 catabolic process Effects 0.000 description 2
- 238000006731 degradation reaction Methods 0.000 description 2
- 229910052742 iron Inorganic materials 0.000 description 2
- 230000004060 metabolic process Effects 0.000 description 2
- 230000005012 migration Effects 0.000 description 2
- 238000013508 migration Methods 0.000 description 2
- 229910052757 nitrogen Inorganic materials 0.000 description 2
- 229910052698 phosphorus Inorganic materials 0.000 description 2
- 239000011574 phosphorus Substances 0.000 description 2
- 230000008439 repair process Effects 0.000 description 2
- 150000003839 salts Chemical class 0.000 description 2
- 239000013049 sediment Substances 0.000 description 2
- 239000010802 sludge Substances 0.000 description 2
- 239000010959 steel Substances 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 238000003911 water pollution Methods 0.000 description 2
- 241000894006 Bacteria Species 0.000 description 1
- 241001465754 Metazoa Species 0.000 description 1
- 241000209504 Poaceae Species 0.000 description 1
- 230000002411 adverse Effects 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 239000013065 commercial product Substances 0.000 description 1
- 230000018109 developmental process Effects 0.000 description 1
- 239000003337 fertilizer Substances 0.000 description 1
- 230000006872 improvement Effects 0.000 description 1
- 239000010842 industrial wastewater Substances 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 230000000813 microbial effect Effects 0.000 description 1
- 230000008520 organization Effects 0.000 description 1
- 239000002957 persistent organic pollutant Substances 0.000 description 1
- 239000000575 pesticide Substances 0.000 description 1
- 230000005080 plant death Effects 0.000 description 1
- 230000008569 process Effects 0.000 description 1
- 230000035755 proliferation Effects 0.000 description 1
- 239000004576 sand Substances 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
- 230000004083 survival effect Effects 0.000 description 1
Images
Classifications
-
- 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
Landscapes
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
Abstract
本实用新型涉及一种黑臭河道治理装置,由垃圾格栅、缓冲隔断和小型人工湿地构成,在两道垃圾格栅的内侧均设有缓冲隔断,垃圾格栅与缓冲隔断之间以及两道缓冲隔断之间均设有推流增氧设备,其中,在上游垃圾格栅与缓冲隔断之间的推流增氧设备的下游设有生物菌种的投放口;在所述两道缓冲隔断之间设有小型人工湿地及生态浮床,所述的浮床由塑料中空框架和固定在中空框架上的渔网构成,浮床上栽种有植物,浮床由固定机构定位在水体中。优点是:为一组合装置,各个分装置均为常见或简单制作而成,成本少、管理费用低、治理效果明显,可使水体中有机物快速降解,有助于建立和修复水环境中的生物链、形成生物多样性和提高水体自净能力。
The utility model relates to a treatment device for black and odorous rivers, which is composed of a garbage grid, a buffer partition and a small artificial wetland. The push-flow aeration equipment is provided between the buffer partitions, and the downstream of the push-flow aeration equipment between the upstream garbage grill and the buffer partition is provided with a drop-in port for biological strains; between the two buffer partitions A small artificial wetland and an ecological floating bed are arranged in between. The floating bed is composed of a plastic hollow frame and a fishing net fixed on the hollow frame. Plants are planted on the floating bed, and the floating bed is positioned in the water body by a fixing mechanism. The advantages are: it is a combined device, each sub-device is made of common or simple, low cost, low management cost, obvious treatment effect, can quickly degrade organic matter in the water body, and help to establish and restore the biological environment in the water environment. chain, form biodiversity and improve the self-purification capacity of water bodies.
Description
技术领域 technical field
本实用新型涉及一种河道治理装置,尤其涉及一种严重污染的黑臭河道的治理装置。The utility model relates to a river course treatment device, in particular to a treatment device for heavily polluted black and smelly river courses.
背景技术 Background technique
近年来,随着工业的发展和人口的增多,人类对水资源的污染越来越严重,重点表现在工业废水、城市生活污水、农田的肥料农药通过点源或非点源的方式输入河流湖泊造成水体污染。此外,人类活动或自然过程向大气排放了一定量的有害物质,通过雨水吸收后降落到地面,和地面被溶解物质一起,通过非点源方式进入河流湖泊再次造成水体污染。特别是一些流动性较差的小水体,长年累月接纳的污染物总量远远超过了其本身具有的自净容量,导致水体发黑发臭、底部淤积严重。随着人们对生活环境质量要求的不断提高,对黑臭河道的治理越来越受到重视。In recent years, with the development of industry and the increase of population, the pollution of water resources by humans has become more and more serious. The focus is on the input of industrial wastewater, urban domestic sewage, and fertilizers and pesticides from farmland into rivers and lakes through point sources or non-point sources. cause water pollution. In addition, human activities or natural processes emit a certain amount of harmful substances into the atmosphere, which are absorbed by rainwater and fall to the ground. Together with dissolved substances on the ground, they enter rivers and lakes through non-point sources and cause water pollution again. Especially for some small water bodies with poor fluidity, the total amount of pollutants received over the years far exceeds their own self-purification capacity, resulting in black and smelly water bodies and serious bottom sedimentation. With the continuous improvement of people's requirements for the quality of living environment, more and more attention has been paid to the control of black and odorous rivers.
发明内容 Contents of the invention
本实用新型所要解决的技术问题在于针对黑臭河道的特点提供一种黑臭河道的治理装置,具有简单易行、投资成本少、运行管理费用低、治理效果明显的特点。The technical problem to be solved by the utility model is to provide a treatment device for black and smelly rivers according to the characteristics of black and smelly rivers, which has the characteristics of simple operation, low investment cost, low operation and management costs, and obvious treatment effect.
本实用新型解决上述技术问题所采取的技术方案是:一种黑臭河道的治理装置,设在待治理河段处,包括拦污截污设施,由垃圾格栅、缓冲隔断和小型人工湿地构成,在待治理河段的水流方向上,上游和下游两端均设有垃圾格栅,在两道垃圾格栅的内侧均设有缓冲隔断,在垃圾格栅与缓冲隔断之间,以及在两道缓冲隔断之间均设有推流增氧设备,其中,在上游垃圾格栅与缓冲隔断之间的推流增氧设备的下游设有生物菌种的投放口;在所述两道缓冲隔断之间设有小型人工湿地及生态浮床,所述的浮床由塑料中空框架和固定在中空框架上的渔网构成,浮床上栽种有植物,浮床由固定机构定位。The technical scheme adopted by the utility model to solve the above-mentioned technical problems is: a treatment device for black and odorous rivers, which is located at the river section to be treated, including sewage interception facilities, which are composed of garbage grids, buffer partitions and small artificial wetlands , in the flow direction of the river section to be treated, there are garbage grills at both ends of the upstream and downstream, buffer partitions are provided inside the two garbage grills, between the garbage grills and buffer partitions, and between the two garbage grills. There are push-flow oxygenation equipment between the buffer partitions, wherein, the downstream of the push-flow oxygenation equipment between the upstream garbage grill and the buffer partition is provided with a drop-in port for biological strains; in the two buffer partitions A small artificial wetland and an ecological floating bed are arranged between them. The floating bed is composed of a plastic hollow frame and a fishing net fixed on the hollow frame. Plants are planted on the floating bed, and the floating bed is positioned by a fixing mechanism.
本实用新型的装置在待治理河段的两端处建立适当的拦污截污预处理装置,在治理河段内适当位置安装适宜的推流增氧设施,投放适量的、安全的、高效生物菌种,在黑臭河道修复至一定程度后引进生物浮床,完善水环境生物链,以遵循自然界本身规律的方式,使水体中的有机物快速降解,实现污染水体水质原位修复和底部有机淤泥原位矿化,逐步建立和修复水环境中的生物链,形成生物多样性,利用培育的动植物、培养接种的微生物的生命活动实现水体中污染物的转移、转化和降解来净化水质、提高水体自净能力。The device of the utility model establishes appropriate pollution-blocking and interception pretreatment devices at both ends of the river section to be treated, and installs suitable push-flow and oxygen-increasing facilities at appropriate positions in the treated river section, and puts in an appropriate amount of safe and high-efficiency biological Bacteria, after the restoration of black and odorous rivers to a certain extent, introduce biological floating beds to improve the biological chain of the water environment, and quickly degrade the organic matter in the water body in a way that follows the laws of nature itself, so as to realize the in-situ restoration of the water quality of the polluted water body and the original organic sludge at the bottom. Site mineralization, gradually establish and restore the biological chain in the water environment, form biodiversity, use the life activities of cultivated animals and plants, cultivated and inoculated microorganisms to realize the transfer, transformation and degradation of pollutants in the water body to purify water quality and improve water quality. Self-cleaning ability.
自投放口投入的微生物必须是经过国家权威机构安全性鉴定的,以经过筛选培育的土著微生物为佳,旨在通过微生物的生命代谢活动,吸收、降解、转化水体中的污染物,消除黑臭,改善水质,提高透明度,促进水体中有机质和营养盐之间的迁移转化,实现河道水体原位修复和底泥原位矿化,恢复水体自我净化的能力。The microorganisms put in from the feeding port must be safety-approved by the national authoritative organization, and the indigenous microorganisms that have been screened and cultivated are preferred. The purpose is to absorb, degrade, and transform pollutants in the water body through the life and metabolism activities of microorganisms, and eliminate black and odor. , Improve water quality, increase transparency, promote the migration and transformation between organic matter and nutrient salts in water, realize in-situ restoration of river water and in-situ mineralization of sediment, and restore the ability of self-purification of water.
在上述方案的基础上,所述的垃圾格栅与缓冲隔断的间距为50~100m。On the basis of the above scheme, the distance between the garbage grill and the buffer partition is 50-100m.
在上述方案的基础上,所述垃圾格栅的形状与河道的断面形状相同,其孔径为10~30mm,其目的在于拦截可能随水流进入的大颗粒物。On the basis of the above solution, the shape of the garbage grill is the same as the section shape of the river, and its aperture is 10-30mm, and its purpose is to intercept large particles that may enter with the water flow.
在上述方案的基础上,所述缓冲隔断的形状与河道的断面形状相同,由土工布、土工布上端缀有的浮球和下端坠有的砂石勒构成,通过多种手段对上游来水进行预反应,削减其污染总量。On the basis of the above scheme, the shape of the buffer partition is the same as the section shape of the river channel, and it is composed of geotextiles, floating balls attached to the upper end of the geotextiles, and sand stones dropped from the lower end. Pre-reaction to reduce the total amount of pollution.
在上述方案的基础上,所述的推流增氧设备为人工瀑布、跌水、喷泉、水车或曝气机(如潜水式曝气机、深水式曝气机、叶轮式曝气机和喷涌式曝气机等),其目的是将空气中的氧气注入水体中,提高水体的溶解氧,湿焚掉水中部分有机物,激活留存在水体中的土著微生物,修复断裂的水体生物链,为生物和微生物的生命活动提供必要的条件。在缓冲隔断和点源污染入口处附近推流增氧设备的设置密度可以高一些、间距可以小一些。On the basis of the above-mentioned scheme, the described plug-flow aeration equipment is artificial waterfall, water drop, fountain, waterwheel or aerator (such as submersible aerator, deep water aerator, impeller aerator and gushing aerator, etc.), the purpose of which is to inject oxygen in the air into the water body, increase the dissolved oxygen in the water body, wet burn some organic matter in the water, activate the indigenous microorganisms remaining in the water body, and repair the broken water body biological chain. Biological and microbial life activities provide the necessary conditions. The density of plug-flow aeration equipment near the buffer partition and point source pollution inlet can be higher and the spacing can be smaller.
在上述方案的基础上,所述的小型人工湿地设在点源污染的入口处,使来水中污染物质随水在湿地缝隙和植物根系中流动时,受物理、化学和生物三重作用而大幅度削减。On the basis of the above scheme, the small-scale constructed wetland is set at the entrance of point source pollution, so that when the pollutants in the incoming water flow with the water in the wetland gaps and plant roots, they will be greatly affected by the triple action of physics, chemistry and biology. reduce.
在上述方案的基础上,所述的生态浮床设在河道中央或两旁,所述中空框架为长2~6米,宽1~2米的矩形中空框架,所述渔网网目为40~50mm,其中,渔网设有一层,栽种的植物为草属类物;或渔网设有二层,栽种的植物为直立型植物。On the basis of the above scheme, the ecological floating bed is arranged in the center or both sides of the river, the hollow frame is a rectangular hollow frame with a length of 2 to 6 meters and a width of 1 to 2 meters, and the mesh of the fishing net is 40 to 50 mm. Wherein, the fishing net is provided with one layer, and the plants planted are grasses; or the fishing net is provided with two layers, and the plants planted are erect plants.
本实用新型的生态浮床是一种主要由水生植物和悬浮生物填料组合而成的生态浮床,目的是在获得经济效益和美化水域景观的同时,通过植物根系的吸附和吸收作用,削减富集在水体中的氮磷及有机污染物质,起到净化水质、令水体变清的作用,并且为微生物提供良好的附着环境,延长微生物的作用时间,强化微生物的作用效果。该设施在受污染水体修复至一定程度后引入,以免植物死亡带入新的污染。The ecological floating bed of the utility model is an ecological floating bed mainly composed of aquatic plants and suspended biological fillers. Nitrogen, phosphorus and organic pollutants in the water body can purify the water quality and make the water body clear, and provide a good attachment environment for microorganisms, prolong the action time of microorganisms, and strengthen the effect of microorganisms. This facility is introduced after the contaminated water body has been rehabilitated to a certain extent, so as to avoid new pollution caused by plant death.
在上述方案的基础上,所述的浮床下方悬挂有悬浮填料球串,由多数个填料球串接构成,该悬浮填料球串的一端固定在中空框架上,另一端固定有重垂物。On the basis of the above solution, a string of suspended filler balls is suspended below the floating bed, which is composed of a plurality of filler balls connected in series. One end of the string of suspended filler balls is fixed on the hollow frame, and the other end is fixed with a weight.
在上述方案的基础上,所述的固定机构包括定位杆和定位环,定位环设置在中空框架上,定位杆穿过定位环后插在水体的河床床底定位。On the basis of the above solution, the fixing mechanism includes a positioning rod and a positioning ring, the positioning ring is arranged on the hollow frame, and the positioning rod passes through the positioning ring and is inserted at the bottom of the riverbed of the water body for positioning.
在上述方案的基础上,所述的固定机构还包括限位绳和固定锚,多数个浮床拼接成组并由限位绳固定,构成组合浮床,限位绳的一端固定有固定锚,固定锚置于水体中定位或与河床固定。On the basis of the above scheme, the fixing mechanism also includes a limit rope and a fixed anchor. A plurality of floating beds are spliced into groups and fixed by a limit rope to form a combined floating bed. One end of the limit rope is fixed with a fixed anchor, and the fixed anchor Placed in a body of water or fixed to a river bed.
本实用新型的有益效果是:The beneficial effects of the utility model are:
1、本实用新型的黑臭河道治理系统装置为一组合装置,各个分装置均为常见市售商品或通过简单制作而成,投资成本少、运行管理费用低、治理效果明显,可使水体中有机物快速降解,实现污染水体水质原位修复和底部有机淤泥原位矿化,有助于建立和修复水环境中的生物链、形成生物多样性和提高水体自净能力;1. The black and odorous river treatment system device of the present utility model is a combination device, and each sub-device is a common commercial product or is made by simple manufacturing. It has low investment cost, low operation and management cost, and obvious treatment effect, which can make the water body The rapid degradation of organic matter can realize the in-situ restoration of polluted water quality and the in-situ mineralization of organic sludge at the bottom, which helps to establish and restore the biological chain in the water environment, form biodiversity and improve the self-purification ability of water bodies;
2、通过在治理河段两端和点源污染入口处建立拦污截污设施,有效拦截来水中的大颗粒杂物,并对夹杂在来水中的污染物进行预处理,减少对治理河段的不利影响;2. Through the establishment of pollution interception facilities at both ends of the treated river section and at the entrance of point source pollution, the large particle debris in the incoming water can be effectively intercepted, and the pollutants mixed in the incoming water can be pretreated to reduce the impact on the treated river section. the adverse effects of
3、可应用多种手段增加水体流动性和溶解氧,湿焚掉水中部分有机物,激活留存在水体中的土著微生物,为水体中的生物和微生物的生命活动提供条件,修复断裂的水体生物链;3. Various methods can be used to increase the fluidity and dissolved oxygen of the water body, wet incinerate some organic matter in the water, activate the indigenous microorganisms remaining in the water body, provide conditions for the life activities of organisms and microorganisms in the water body, and repair the broken water body biological chain ;
4、设置生物菌种的投放口,通过投放的生物菌种的生命代谢活动,吸收、降解、转化水体中的污染物,消除黑臭,改善水质,提高透明度,促进水体中有机质和营养盐之间的迁移转化,实现河道水体原位修复和底泥原位矿化,恢复水体自我净化的能力;4. Set up the feeding port of biological strains, absorb, degrade, and transform pollutants in the water body through the life metabolism activities of the biological strains put in, eliminate black odor, improve water quality, increase transparency, and promote the relationship between organic matter and nutrient salts in the water body. In-situ migration and transformation of river water, in-situ restoration of river water and in-situ mineralization of sediment, restore the ability of self-purification of water;
5、通过生态浮床上种植的水生植物的生命活动,可吸收转化水体中部分营养盐和有机物,降低氮磷浓度,为微生物提供良好的附着载体,帮助形成优势群落,恢复水体自净能力。5. Through the life activities of aquatic plants planted on the ecological floating bed, it can absorb and transform some nutrients and organic matter in the water body, reduce the concentration of nitrogen and phosphorus, provide a good attachment carrier for microorganisms, help form dominant communities, and restore the self-purification ability of water bodies.
附图说明 Description of drawings
图1为本实用新型的俯视结构示意图。Fig. 1 is a top view structural diagram of the utility model.
图2为本实用新型垃圾格栅的结构示意图。Fig. 2 is a schematic diagram of the structure of the garbage grill of the present invention.
图3为本实用新型缓冲隔断的结构示意图。Fig. 3 is a structural schematic diagram of the buffer partition of the present invention.
图4为本实用新型小型人工湿地的结构示意图。Fig. 4 is a schematic diagram of the structure of the small constructed wetland of the present invention.
图5为本实用新型生态浮床的结构示意图。Fig. 5 is a structural schematic diagram of the utility model ecological floating bed.
附图中标号说明Explanation of the numbers in the drawings
1-治理装置1- Governance device
11-垃圾格栅 111-扁钢 112-镀锌铁网11-Garbage grate 111-Flat steel 112-Galvanized iron mesh
12-缓冲隔断 121-浮球 122-土工布12-buffer partition 121-float 122-geotextile
123-砂石勒123-Sandstone Le
13-小型人工湿地 131-植物 132-上层土壤13-Small Constructed Wetland 131-Plant 132-Upper Soil
133-砾石填料 134-下层土壤133- Gravel Fill 134- Subsoil
2-推流增氧设备 3-投放口2-Push flow oxygenation equipment 3-Loading port
4-生态浮床 41-渔网 42-中空框架4-ecological floating bed 41-fishing net 42-hollow frame
43-植物 44-悬浮填料球串 45-限位绳43-Plant 44-Suspended filler ball string 45-Limiting rope
46-定位杆 47-固定锚46-Position rod 47-Fixed anchor
具体实施方式 Detailed ways
以下结合附图对本实用新型作进一步说明。Below in conjunction with accompanying drawing, the utility model is further described.
请参阅图1至图5所示,一种黑臭河道治理装置,设在待治理河段处,包括拦污截污设施1,由垃圾格栅11、缓冲隔断12和小型人工湿地13构成,在待治理河段的水流方向上,上游和下游两端均设有垃圾格栅11,在两道垃圾格栅11的内侧50~100m处均设有缓冲隔断12,在垃圾格栅11与缓冲隔断12之间,以及在两道缓冲隔断12之间均设有推流增氧设备2,为人工瀑布、跌水、喷泉、水车或曝气机。Please refer to Fig. 1 to Fig. 5, a kind of black and smelly river treatment device is located at the section of the river to be treated, including the sewage interception facility 1, which is composed of a
在垃圾格栅11与缓冲隔断12之间的推流增氧设备2下游设有生物菌种的投放口3,将生物菌种投放在靠近该推流增氧设备2的作用区域中,这样有利于生物菌种扩散和生长,第一次投放要在曝气增氧一段时间后进行。在治理初期,治理段水质较差,投放的时间间隔短一些、投放量多一些;在治理段水质改善后,投放的时间间隔长一些、投放量少一些,最终逐渐缩减到零。The downstream of the push-flow aeration equipment 2 between the
垃圾格栅11用扁钢111和镀锌铁网112制成,其形状为与河道断面形状相同的上宽下窄的倒梯形,用以拦截随水流可能进入治理段的大颗粒物,垃圾格栅11其孔径为10~30mm。
缓冲隔断12由土工布122、土工布122上端缀有的浮球121和下端坠有的砂石勒123构成,其形状为与河道断面形状相同的上宽下窄的倒梯形,砂石勒123保证其与河床底部紧密贴合,浮球121保证其适应不同水位高度的变化。The
在两道缓冲隔断12之间设有小型人工湿地13,设在点源污染的入口处(必要时也可在治理段外设置),它是一个有一定长宽比的、底面有一定坡度的洼地,用上层土壤132、砾石填料133和下层土壤134混合组成填料床,上层土壤132表面种植具有性能良好、成活率高、抗水性强、生长周期长、美观且具有一定经济价值的水生植物131,使来水中的污染物在床体填料缝隙和植物根系中流动时得到削减。There is a small
所述的生态浮床4设在两道缓冲隔断12之间治理段水质较佳处,可沿河道设置在两旁,由塑料中空框架42和固定在中空框架42上的一层或二层渔网41构成,中空框架为长2~6米,宽1~2米的矩形中空框架,所述的渔网网目为40~50mm,浮床上栽种有植物43,浮床由固定机构定位;Described ecological floating
所述的中空框架42下方悬挂有悬浮填料球串44,由多数个填料球串接构成,该悬浮填料球串44的一端固定在中空框架42上,另一端固定有重垂物,保证其在水中始终保持下垂状态;Suspended
所述的固定机构包括定位杆46、定位环(图中未示)、限位绳45和固定锚47,定位环设置在矩形中空框架42的四个角内侧,定位杆46穿过定位环后插在待治理河道的河床床底定位,多数个生态浮床4拼接成组并由限位绳45固定,构成组合浮床,限位绳45的一端固定有固定锚47,固定锚47置于水体中定位,以防止浮床随水漂移。Described fixing mechanism comprises locating
Claims (10)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN2009200699858U CN201406359Y (en) | 2009-04-07 | 2009-04-07 | Treatment device for black and odorous river course |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN2009200699858U CN201406359Y (en) | 2009-04-07 | 2009-04-07 | Treatment device for black and odorous river course |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN201406359Y true CN201406359Y (en) | 2010-02-17 |
Family
ID=41677290
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN2009200699858U Expired - Fee Related CN201406359Y (en) | 2009-04-07 | 2009-04-07 | Treatment device for black and odorous river course |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN201406359Y (en) |
Cited By (24)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101913708A (en) * | 2010-09-08 | 2010-12-15 | 乔世琴 | Low-carbon and energy-saving method for controlling polluted water quality of lakes or landscape lakes |
| CN103224295A (en) * | 2013-05-15 | 2013-07-31 | 北京师范大学 | Automatic suction and ecological treatment system for polluted bottom sediments of rivers |
| CN103224314A (en) * | 2013-05-15 | 2013-07-31 | 北京师范大学 | River sediment automatic suction device |
| CN103332789A (en) * | 2013-06-06 | 2013-10-02 | 惠州市东江园林工程有限公司 | Method for ecologically purifying black and odorous riverway water body |
| CN104003514A (en) * | 2014-04-13 | 2014-08-27 | 北京工业大学 | Bio-contact oxidation device for polluted river water purification |
| CN104230100A (en) * | 2014-09-04 | 2014-12-24 | 上海汀滢环保科技有限公司 | Three-dimensional ecological corridor system and method for in-situ restoration of river water body |
| CN104671419A (en) * | 2015-03-04 | 2015-06-03 | 重庆文理学院 | Energy-saving bending-flow type denitrification floating island |
| CN104773897A (en) * | 2014-01-13 | 2015-07-15 | 中国科学院烟台海岸带研究所 | Coast lack-odor river channel water quality in-situ remediation system |
| CN104803557A (en) * | 2015-04-17 | 2015-07-29 | 苏州绿世界园林发展有限公司 | Compound type ditch pond wetland system with functions of farmland drainage purification and ecological restoration |
| CN105152352A (en) * | 2015-10-12 | 2015-12-16 | 朱学红 | River course black foul water biological purification treatment device |
| CN105585138A (en) * | 2016-02-29 | 2016-05-18 | 北京英特环科水处理工程设备有限公司 | MANWMB (micro nano aeration wastewater microbial bioremediation) system for black and odorous river control and control method thereof |
| CN105648974A (en) * | 2014-12-02 | 2016-06-08 | 中国科学院烟台海岸带研究所 | In-situ desilting, oxygen aeration and landscape construction method of polluted riverway |
| CN106045055A (en) * | 2016-07-08 | 2016-10-26 | 武汉理工大学 | Ecological restoration device and method for urban black-odor riverway |
| CN106517672A (en) * | 2016-12-21 | 2017-03-22 | 广州绿日环保科技有限公司 | Sewage interception and ecological floating bed integrated system |
| CN107188318A (en) * | 2017-05-18 | 2017-09-22 | 长江大学 | A kind of black-odor riverway waste water control method |
| CN107487940A (en) * | 2017-09-07 | 2017-12-19 | 广州市天瑞环保科技有限公司 | A kind of sewage disposal system and method to city river |
| CN108264198A (en) * | 2018-02-01 | 2018-07-10 | 宁波立升环保工程有限公司 | A kind of administering method in water pollution river |
| WO2018129896A1 (en) * | 2017-01-11 | 2018-07-19 | 深圳市碧园环保技术有限公司 | Artificial wetland system for advanced treatment of tail water from sewage treatment plant |
| CN108483668A (en) * | 2017-12-20 | 2018-09-04 | 中山市和智电子科技有限公司 | Black and odorous water body treatment system |
| CN108585361A (en) * | 2017-12-20 | 2018-09-28 | 中山市和智电子科技有限公司 | Black and odorous water body treatment system |
| CN110294532A (en) * | 2019-08-06 | 2019-10-01 | 西南科技大学 | A kind of chinampa that shock resistance is strong |
| CN114477470A (en) * | 2022-02-11 | 2022-05-13 | 安阳工学院 | A sewage treatment type microbial injection device that automatically monitors the state of water pollution |
| CN115385516A (en) * | 2021-05-25 | 2022-11-25 | 南京溧水水务集团有限公司 | Water quality purification system and method |
| CN116022928A (en) * | 2023-01-05 | 2023-04-28 | 中国科学院城市环境研究所 | A constructed wetland and a method for efficient removal of total nitrogen from dispersed sewage used in reservoir rivers |
-
2009
- 2009-04-07 CN CN2009200699858U patent/CN201406359Y/en not_active Expired - Fee Related
Cited By (34)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101913708B (en) * | 2010-09-08 | 2014-07-16 | 乔世琴 | Low-carbon energy-saving method for treating polluted water quality of lake or landscape lake |
| CN101913708A (en) * | 2010-09-08 | 2010-12-15 | 乔世琴 | Low-carbon and energy-saving method for controlling polluted water quality of lakes or landscape lakes |
| CN103224295A (en) * | 2013-05-15 | 2013-07-31 | 北京师范大学 | Automatic suction and ecological treatment system for polluted bottom sediments of rivers |
| CN103224314A (en) * | 2013-05-15 | 2013-07-31 | 北京师范大学 | River sediment automatic suction device |
| CN103332789B (en) * | 2013-06-06 | 2014-11-26 | 惠州市东江园林工程有限公司 | Method for ecologically purifying black and odorous riverway water body |
| CN103332789A (en) * | 2013-06-06 | 2013-10-02 | 惠州市东江园林工程有限公司 | Method for ecologically purifying black and odorous riverway water body |
| CN104773897A (en) * | 2014-01-13 | 2015-07-15 | 中国科学院烟台海岸带研究所 | Coast lack-odor river channel water quality in-situ remediation system |
| CN104773897B (en) * | 2014-01-13 | 2016-06-15 | 中国科学院烟台海岸带研究所 | A kind of water quality in-situ remediation system of strand black-odor riverway |
| CN104003514A (en) * | 2014-04-13 | 2014-08-27 | 北京工业大学 | Bio-contact oxidation device for polluted river water purification |
| CN104230100A (en) * | 2014-09-04 | 2014-12-24 | 上海汀滢环保科技有限公司 | Three-dimensional ecological corridor system and method for in-situ restoration of river water body |
| CN104230100B (en) * | 2014-09-04 | 2017-01-11 | 上海汀滢环保科技有限公司 | Three-dimensional ecological corridor system and method for in-situ restoration of river water body |
| CN105648974A (en) * | 2014-12-02 | 2016-06-08 | 中国科学院烟台海岸带研究所 | In-situ desilting, oxygen aeration and landscape construction method of polluted riverway |
| CN105648974B (en) * | 2014-12-02 | 2017-12-19 | 中国科学院烟台海岸带研究所 | Desilting in situ, oxygenation and the Scene construction method of a kind of polluted river channel |
| CN104671419A (en) * | 2015-03-04 | 2015-06-03 | 重庆文理学院 | Energy-saving bending-flow type denitrification floating island |
| CN104671419B (en) * | 2015-03-04 | 2017-08-25 | 重庆文理学院 | Energy-saving deflector type denitrogenation chinampa |
| CN104803557A (en) * | 2015-04-17 | 2015-07-29 | 苏州绿世界园林发展有限公司 | Compound type ditch pond wetland system with functions of farmland drainage purification and ecological restoration |
| CN105152352A (en) * | 2015-10-12 | 2015-12-16 | 朱学红 | River course black foul water biological purification treatment device |
| CN105585138A (en) * | 2016-02-29 | 2016-05-18 | 北京英特环科水处理工程设备有限公司 | MANWMB (micro nano aeration wastewater microbial bioremediation) system for black and odorous river control and control method thereof |
| CN105585138B (en) * | 2016-02-29 | 2019-01-18 | 北京英特环科水处理工程设备有限公司 | A kind of the MNAWMB system and its administering method of black-odor riverway improvement |
| CN106045055A (en) * | 2016-07-08 | 2016-10-26 | 武汉理工大学 | Ecological restoration device and method for urban black-odor riverway |
| CN106045055B (en) * | 2016-07-08 | 2019-07-12 | 武汉理工大学 | A kind of ecological restoration device and method of city black-odor riverway |
| CN106517672A (en) * | 2016-12-21 | 2017-03-22 | 广州绿日环保科技有限公司 | Sewage interception and ecological floating bed integrated system |
| WO2018129896A1 (en) * | 2017-01-11 | 2018-07-19 | 深圳市碧园环保技术有限公司 | Artificial wetland system for advanced treatment of tail water from sewage treatment plant |
| CN107188318B (en) * | 2017-05-18 | 2020-10-20 | 长江大学 | Black and odorous river sewage treatment method |
| CN107188318A (en) * | 2017-05-18 | 2017-09-22 | 长江大学 | A kind of black-odor riverway waste water control method |
| CN107487940A (en) * | 2017-09-07 | 2017-12-19 | 广州市天瑞环保科技有限公司 | A kind of sewage disposal system and method to city river |
| CN108483668A (en) * | 2017-12-20 | 2018-09-04 | 中山市和智电子科技有限公司 | Black and odorous water body treatment system |
| CN108585361A (en) * | 2017-12-20 | 2018-09-28 | 中山市和智电子科技有限公司 | Black and odorous water body treatment system |
| CN108264198A (en) * | 2018-02-01 | 2018-07-10 | 宁波立升环保工程有限公司 | A kind of administering method in water pollution river |
| CN110294532A (en) * | 2019-08-06 | 2019-10-01 | 西南科技大学 | A kind of chinampa that shock resistance is strong |
| CN110294532B (en) * | 2019-08-06 | 2024-05-10 | 西南科技大学 | Floating island with strong impact resistance |
| CN115385516A (en) * | 2021-05-25 | 2022-11-25 | 南京溧水水务集团有限公司 | Water quality purification system and method |
| CN114477470A (en) * | 2022-02-11 | 2022-05-13 | 安阳工学院 | A sewage treatment type microbial injection device that automatically monitors the state of water pollution |
| CN116022928A (en) * | 2023-01-05 | 2023-04-28 | 中国科学院城市环境研究所 | A constructed wetland and a method for efficient removal of total nitrogen from dispersed sewage used in reservoir rivers |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN201406359Y (en) | Treatment device for black and odorous river course | |
| CN106186343B (en) | A kind of comprehensive processing method to urban river | |
| CN100378272C (en) | Stereo in-situ ecological urban water system repairing process | |
| CN105330107B (en) | A kind of urban waterway water purification system and purification method | |
| CN101318718B (en) | Bionic reinforced scouring method for landscape water environment | |
| CN104496106B (en) | A campus rainwater ecological purification integrated treatment method and ecological purification integrated system | |
| CN105000749B (en) | A kind of ecological restoring method in situ and system and application suitable for tidal interior River system sewage draining exit sewage | |
| CN102874934A (en) | Technology for direct in-situ treatment and ecological restoration of polluted water body | |
| CN204356190U (en) | A kind of campus rainwater ecological purifying integral system | |
| CN104926032A (en) | Multistage compound strengthening and purifying method for tidal waterway in coastal city | |
| CN102249419A (en) | Combined repairing technology system for various combined technologies of regenerated water landscape riverway water body | |
| CN106006965A (en) | Black and odorous water body treatment and restoration system | |
| CN105565511B (en) | A kind of black-odor riverway renovation technique and distribution device reducing foul smell loss | |
| CN105502828A (en) | Oligodynamic in-situ ecological restoration method of urban beheaded river | |
| CN109319934A (en) | An ecological restoration method of river water body in farmland catchment area | |
| CN104058545B (en) | A method for treating aquaculture sewage by combining biological carrier and ecological restoration technology | |
| CN106746229A (en) | A kind of Drain contamination for river channel mouthful cuts the purified in situ processing method and system of dirty water conservancy diversion | |
| CN208776519U (en) | A kind of artificial swamp multistage reinforcing pool sewage disposal system | |
| CN204185336U (en) | For the stereo ecological gallery system of river water body in-situ immobilization | |
| CN103043796A (en) | Inland riverbank vegetation buffering and purifying zone | |
| CN108996703B (en) | An ecological restoration system for black and odorous water, soil and water cycle | |
| CN109879444A (en) | A kind of composite artificial water plant and ecological ball device and application method | |
| CN205740506U (en) | Black and odorous water body treatment and restoration system | |
| CN206328294U (en) | A kind of Drain contamination for river channel mouthful cuts the purified in situ processing system of dirty water conservancy diversion | |
| CN110885161B (en) | Water quality purification and ecological construction system for lake and pond water body and implementation method thereof |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| C14 | Grant of patent or utility model | ||
| GR01 | Patent grant | ||
| C17 | Cessation of patent right | ||
| CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20100217 Termination date: 20120407 |