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CN105366817A - Multi-stage filler constructed wetland construction method - Google Patents

Multi-stage filler constructed wetland construction method Download PDF

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Publication number
CN105366817A
CN105366817A CN201510828544.1A CN201510828544A CN105366817A CN 105366817 A CN105366817 A CN 105366817A CN 201510828544 A CN201510828544 A CN 201510828544A CN 105366817 A CN105366817 A CN 105366817A
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wetland
water
tail water
bed
tail
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张文艺
陈晶
何敏
张伟
王莉娜
许燕峰
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Changzhou University
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Changzhou University
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/32Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2301/00General aspects of water treatment
    • C02F2301/08Multistage treatments, e.g. repetition of the same process step under different conditions
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

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  • Life Sciences & Earth Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Biotechnology (AREA)
  • Botany (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Microbiology (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
  • Hydroponics (AREA)

Abstract

本发明属于生态与环境保护领域,涉及一种多级填料人工湿地建造方法。该方法所建造的水平潜流式多级填料人工湿地,以逐级填充砾石、红砖碎块、钢渣、陶粒和粘土作为湿地填料,并交错种植茭白、梭鱼草、黑麦草与红叶石楠作为湿地植物,通过填料过滤吸附、植物吸收和微生物分解的综合作用,有效地深度净化城市污水厂尾水。湿地的深度、池体长度和宽度可根据不同处理尾水量进行设置。本发明的多级填料人工湿地建造方法具有投资少、成本低、处理效果稳定、运行管理方便等特点。The invention belongs to the field of ecology and environmental protection, and relates to a method for constructing a multi-stage filler artificial wetland. The horizontal submerged multi-stage filler artificial wetland constructed by this method uses gravel, red brick fragments, steel slag, ceramsite and clay as wetland fillers step by step, and is interlaced with water bamboo, pikegrass, ryegrass and Photinia fruticosa. Wetland plants can effectively purify the tail water of urban sewage plants through the combined effects of filler filtration adsorption, plant absorption and microbial decomposition. The depth of the wetland, the length and width of the pool body can be set according to the amount of tail water to be treated. The construction method of the multi-stage filler constructed wetland of the present invention has the characteristics of less investment, low cost, stable treatment effect, convenient operation and management, and the like.

Description

一种多级填料人工湿地建造方法A method for constructing multi-stage filler artificial wetland

技术领域technical field

本发明属于生态与环境保护领域,具体涉及一种多级填料人工湿地建造方法。The invention belongs to the field of ecology and environmental protection, and in particular relates to a method for constructing a multi-stage filler artificial wetland.

背景技术Background technique

目前,我国城市污水厂一般将尾水就近排入该厂附近的河浜,造成尾水排放口周围的河浜部分区域水生环境受到严重破坏,例如排放尾水即使达到《城镇污水处理厂污染物排放标准》(GB18918-2002)I级A水质标准,仍远高于《地表水环境质量标准》(GB3838-2002)V类水质标准,即《城镇污水处理厂污染物排放标准》(GB18918-2002)一级A的NH3-N、COD、TN、TP排放标准为5.0mg/L、50mg/L、15mg/L、0.5mg/L,而《地表水环境质量标准》(GB3838-2002)V类水的NH3-N、COD、TN、TP标准为2.0mg/L、40mg/L、2.0mg/L、0.4mg/L。考虑到传统潜流式湿地系统净化效率偏低,而多级湿地联用又会造成基建成本高、占地面积大、运行管理难度大。因此,本发明构建一种对城市污水厂尾水有较高深度净化能力、管理维护简单、能耗低的多级填料潜流人工湿地,这对解决由尾水排放而导致的部分地表水污染这一难题意义重大。At present, China's urban sewage plants generally discharge the tail water into the nearby riverside of the plant, causing serious damage to the aquatic environment in some areas of the riverside around the tail water discharge outlet. Discharge Standards" (GB18918-2002) Class I A water quality standards, still far higher than the "Surface Water Environmental Quality Standards" (GB3838-2002) Class V water quality standards, that is, "Pollutant Discharge Standards for Urban Sewage Treatment Plants" (GB18918-2002 ) The NH 3 -N, COD, TN, and TP discharge standards of Class A are 5.0mg/L, 50mg/L, 15mg/L, and 0.5mg/L, while "Surface Water Environmental Quality Standards" (GB3838-2002) V The NH 3 -N, COD, TN, and TP standards for water-like water are 2.0mg/L, 40mg/L, 2.0mg/L, and 0.4mg/L. Considering that the purification efficiency of the traditional subsurface wetland system is relatively low, and the combined use of multi-stage wetlands will result in high infrastructure costs, large land occupation, and difficult operation and management. Therefore, the present invention constructs a multi-stage filler underflow artificial wetland with high deep purification ability for tail water of urban sewage plants, simple management and maintenance, and low energy consumption, which is helpful to solve the problem of partial surface water pollution caused by tail water discharge. One problem is significant.

发明内容Contents of the invention

本发明的目的是解决传统潜流式湿地系统净化效率偏低和多级湿地联用的不足而提供一种多级填料人工湿地建造方法。本发明所构建的水平潜流式多级填料人工湿地以逐级填充砾石、红砖碎块、钢渣、陶粒和粘土作为湿地填料;并交错种植茭白、梭鱼草、黑麦草与红叶石楠作为湿地植物,通过填料过滤吸附、植物吸收和微生物分解的综合作用,有效地深度净化城市污水厂尾水,具有投资少、成本低、处理效果稳定、运行管理方便等特点。The purpose of the present invention is to solve the low purification efficiency of the traditional subsurface wetland system and the deficiency of multi-level wetland combination, and provide a multi-level filler artificial wetland construction method. The horizontal underflow type multi-stage filler artificial wetland constructed by the present invention uses gravel, red brick fragments, steel slag, ceramsite and clay as wetland fillers step by step; and interlaced planting of asparagus, pikegrass, ryegrass and Photinia fragrans as wetlands Plants, through the combined effects of filler filtration and adsorption, plant absorption and microbial decomposition, can effectively purify the tail water of urban sewage plants in depth. It has the characteristics of low investment, low cost, stable treatment effect, and convenient operation and management.

本发明采用的技术方案是:The technical scheme adopted in the present invention is:

一种可深度净化城市污水厂尾水的多级填料人工湿地系统如图1、图2、图3所示:多级填料潜流式人工湿地整体规格为长×宽×深(L×B×H),共分为5个区域,沿尾水水流方向依次构建长度为L1的集水池I、长度为L2的配水槽II、长度为L3的湿地床体区III、长度为L4的沉淀区VI与长度为L5的清水池V,其整体由三七墙砖砌而成,其中配水槽与沉淀区分别用二四砖砌布水墙隔开(墙上布有小孔)。污水处理厂尾水经水管收集通过调节阀门引入集水池汇集后,经溢流堰1溢流进入在配水槽内,再经其后端布水墙2对尾水进行均质均量,进入装有拔风管3的湿地床体区联合物理、化学、生物方法对尾水进行深度净化处理,其后处理水自流通过布水墙均质均量来到沉淀区沉淀去除大颗粒杂质,再经溢流堰溢流汇集于清水池,控制阀门将处理后的尾水外排。A multi-stage filler constructed wetland system capable of deeply purifying the tail water of urban sewage plants is shown in Figure 1, Figure 2, and Figure 3: the overall specification of the multi-stage filler subsurface flow constructed wetland is length×width×depth (L×B×H ), which are divided into 5 areas. Along the direction of the tailwater flow, a sump I with a length of L1, a water distribution channel II with a length of L2, a wetland bed area III with a length of L3, a sedimentation area VI with a length of L4 and The clear water pool V with a length of L5 is made of notoginseng wall bricks as a whole, and the water distribution tank and the sedimentation area are separated by two or four brick water distribution walls (with small holes on the wall). The tail water of the sewage treatment plant is collected through the water pipe and introduced into the sump through the regulating valve. After being collected, it overflows through the overflow weir 1 and enters the water distribution tank. The wetland bed area with the wind pipe 3 is combined with physical, chemical and biological methods to carry out deep purification treatment of the tail water, and then the treated water flows by itself through the water distribution wall to the sedimentation area to precipitate and remove large particles of impurities. The overflow of the overflow weir is collected in the clean water tank, and the control valve discharges the treated tail water.

湿地床体区依次填充厚度为H1的粒径40-50mm砾石、厚度为H2的粒径20-40mm红砖碎块、厚度为H3的粒径8-10mm钢渣、厚度为H4的粒径4-8mm陶粒、加厚度为H5的粘土层(每层用网格1mm×1mm的纱网隔开)来构建湿地填料,床底坡度1%。湿地床搭配种植茭白、红叶石楠、梭鱼草和黑麦草,并且安置有拔风管。在本发明中人工湿地选用生长期的茭白、梭鱼草、黑麦草与红叶石楠进行移植,植物移植后立即进水,使水面接近于湿地表层土壤,1周后湿地植物开始恢复生长,从而让移植植物适应人工湿地系统的环境并生长和湿地床的挂膜。The wetland bed area is filled sequentially with gravel with a particle size of 40-50 mm in thickness H1, red brick fragments with a particle size of 20-40 mm in thickness H2, steel slag with a particle size of 8-10 mm in thickness H3, and 4- 8mm ceramsite, add a clay layer with a thickness of H5 (each layer is separated by a 1mm×1mm gauze) to construct the wetland filler, and the bottom slope of the bed is 1%. The wetland bed is planted with water bamboo, heather, pikegrass and ryegrass, and the windpipe is installed. In the present invention, the artificial wetland is transplanted with wild rice stems, pikegrass, ryegrass and Photinia fragrans in the growth period. Immediately after the plants are transplanted, water is added to make the water surface close to the surface soil of the wetland. After one week, the wetland plants begin to resume growth, thereby allowing the Transplanted plants adapt to the environment of the constructed wetland system and grow and hang film on the wetland bed.

本发明的主要原理基于以下两个方面:The main principle of the present invention is based on the following two aspects:

其一是,本发明采用砾石、红砖碎块、钢渣、陶粒和土壤作为湿地填料,既有利于截留、吸附尾水中的污染物,又有利于在湿地基质表面及其孔隙中形成生物膜,生物膜中的微生物摄取尾水中污染物用于自身生长繁殖和新陈代谢,实现尾水在湿地填料区域中的净化。One is that the present invention uses gravel, red brick fragments, steel slag, ceramsite and soil as wetland fillers, which is not only conducive to intercepting and adsorbing pollutants in tail water, but also conducive to the formation of biofilm on the surface of wetland matrix and its pores , the microorganisms in the biofilm ingest the pollutants in the tail water for their own growth, reproduction and metabolism, so as to realize the purification of the tail water in the wetland fill area.

其二是,本发明交错种植茭白、梭鱼草、黑麦草与红叶石楠作为湿地植物,综合运用植物吸收和根际微生物代谢作用,对尾水水质进行有效净化。The second is that the present invention alternately plants wild rice stems, pikegrass, ryegrass, and Photinia frondosa as wetland plants, and comprehensively utilizes plant absorption and rhizosphere microbial metabolism to effectively purify the water quality of the tail water.

本发明具有以下优势:The present invention has the following advantages:

(1)本发明的湿地床中依次填充砾石、红砖碎块、钢渣、陶粒、土壤作为湿地填料,改进了传统湿地填料层组合,使其更适应尾水的水力条件。从水处理效果来看,本发明制作的湿地床较之单级或二级填料湿地,其对城市污水厂尾水深度净化的能力有所提高。而且湿地填料中红砖碎块混合较高,而红砖碎块便宜易得,如可以使用城市拆迁改造中的废弃房屋砖头。(1) The wetland bed of the present invention is sequentially filled with gravel, red brick fragments, steel slag, ceramsite, and soil as wetland filler, which improves the combination of traditional wetland filler layers and makes it more suitable for the hydraulic conditions of the tail water. From the perspective of water treatment effect, compared with single-stage or two-stage filled wetlands, the wetland bed produced by the present invention has improved ability of deep purification of tail water of urban sewage plants. Moreover, the mix of red brick fragments in the wetland filler is relatively high, and the red brick fragments are cheap and easy to get, such as bricks from abandoned houses in urban demolition and reconstruction.

(2)采用间歇交替运行方式,既有效提高复氧水平,有可有效避免湿地堵塞。通过构建多级填料人工湿地系统,有效地深度净化城市污水厂尾水,其中CODCr能够降至20.50~26.10mg/L;TP能够降至0.19~0.63mg/L;TN能够降至0.74~8.10mg/L;NH4 +-N能够降至0.01~0.35mg/L,具有投资少、成本低、处理效果稳定、运行管理方便等特点。(2) The intermittent and alternating operation mode is adopted, which not only effectively improves the reoxygenation level, but also effectively avoids wetland blockage. By constructing a multi-stage filler artificial wetland system, the tail water of urban sewage plants can be effectively purified in depth, in which COD Cr can be reduced to 20.50-26.10 mg/L; TP can be reduced to 0.19-0.63 mg/L; TN can be reduced to 0.74-8.10 mg/L; NH 4 + -N can be reduced to 0.01~0.35mg/L, which has the characteristics of less investment, low cost, stable treatment effect, and convenient operation and management.

附图说明Description of drawings

图1为多级填料人工湿地系统的平面布置图。Figure 1 is the plan layout of the multi-stage filler constructed wetland system.

其中:I-集水池;II-配水槽;III-湿地床体区;IV-沉淀区;V-清水池;1-茭白;2-红叶石楠;3-梭鱼草;4-黑麦草;Among them: I-collection pool; II-water distribution tank; III-wetland bed area; IV-sedimentation area; V-clear water pool;

L-多级填料人工湿地系统的长度;B-多级填料人工湿地系统的宽度。L-the length of the multi-stage fill constructed wetland system; B-the width of the multi-stage fill constructed wetland system.

图2为多级填料人工湿地系统的剖面图。Figure 2 is a cross-sectional view of the multi-stage filler constructed wetland system.

其中:1-溢流堰;2-布水墙(墙上布有间距为300mm的孔径为20mm的小孔);3-拔风管;Among them: 1-overflow weir; 2-water distribution wall (the wall is covered with small holes with a spacing of 300mm and a diameter of 20mm); 3-exhaust air pipe;

L1-集水池I的长度;L2-配水槽II的长度;L3-湿地床体区III的长度;L4-沉淀区IV的长度;L5-清水池V的长度。L1-the length of the water collection tank I; L2-the length of the water distribution tank II; L3-the length of the wetland bed area III; L4-the length of the precipitation area IV; L5-the length of the clear water tank V.

图3为人工湿地内部湿地基质结构剖面图。Figure 3 is a cross-sectional view of the wetland matrix structure inside the constructed wetland.

其中:H1-粒径40~50mm的砾石层厚度;H2-粒径20~40mm的红砖碎块层厚度;H3-粒径8~10mm的钢渣层厚度;H4-粒径4~8mm的陶粒层厚度;H5-粘土层厚度。Among them: H1-the thickness of the gravel layer with a particle size of 40-50 mm; H2-the thickness of the red brick fragment layer with a particle size of 20-40 mm; H3-the thickness of the steel slag layer with a particle size of 8-10 mm; Granular layer thickness; H5-clay layer thickness.

具体实施方式detailed description

下面结合附图和实施例对本发明作进一步说明。The present invention will be further described below in conjunction with drawings and embodiments.

如图1、图2及图3所示,多级填料潜流式人工湿地整体规格为L×B×H,其分为5个区域,沿尾水水流方向依次构建长度为L1的集水池I、长度为L2的配水槽II、长度为L3的湿地床体区III、长度为L4的沉淀区IV与长度为L5的清水池V,其整体由三七墙砖砌而成,其中配水槽与沉淀区分别用二四砖砌布水墙和隔开(墙上布有间距为300mm的孔径为20mm的小孔)。湿地床体区依次填充厚度为H1的粒径40-50mm砾石、厚度为H2的粒径20-40mm红砖碎块、厚度为H3的粒径8-10mm钢渣、厚度为H4的粒径4-8mm陶粒和厚度为H5的粘土层(每层用网格1mm×1mm的纱网隔开)来构建湿地填料,床底坡度1%。湿地床搭配种植茭白、红叶石楠、梭鱼草和黑麦草,并且安置有拔风管3。污水处理厂尾水经水管收集通过调节阀门引入集水池汇集后,经溢流堰1溢流进入在配水槽内,再经其后端布水墙2对尾水进行均质均量,进入湿地床体区联合物理、化学、生物方法对尾水进行深度净化处理,其后处理水自流通过布水墙均质均量来到沉淀区沉淀去除大颗粒杂质,再经溢流堰溢流汇集于清水池,控制阀门将处理后的尾水外排。As shown in Fig. 1, Fig. 2 and Fig. 3, the overall specification of multi-stage filler submerged flow constructed wetland is L×B×H, which is divided into five areas, and the sump pools I and The water distribution tank II with a length of L2, the wetland bed area III with a length of L3, the sedimentation area IV with a length of L4, and the clear water pool V with a length of L5 are made of Panax notoginseng bricks as a whole, and the water distribution tank and the sedimentation area The districts are separated by two or four brick water walls (the walls are covered with small holes with a spacing of 300mm and a diameter of 20mm). The wetland bed area is filled sequentially with gravel with a particle size of 40-50 mm in thickness H1, red brick fragments with a particle size of 20-40 mm in thickness H2, steel slag with a particle size of 8-10 mm in thickness H3, and 4- 8mm ceramsite and a clay layer with a thickness of H5 (each layer is separated by a 1mm×1mm gauze) are used to construct the wetland filler, and the slope of the bed bottom is 1%. The wetland bed is planted with water bamboo, Photinia fragrans, pikegrass and ryegrass, and the windpipe 3 is installed. The tail water of the sewage treatment plant is collected through the water pipe and introduced into the sump through the regulating valve. After being collected, it overflows through the overflow weir 1 and enters the water distribution tank, and then the tail water is homogenized and equalized by the water distribution wall 2 at the rear end, and enters the wetland. The bed area combines physical, chemical, and biological methods to carry out deep purification treatment of tail water, and then the treated water flows through the water distribution wall to the sedimentation area to precipitate and remove large particles of impurities, and then overflows through the overflow weir and collects in the In the clear water tank, the control valve discharges the treated tail water.

人工湿地选用茭白、梭鱼草、黑麦草与红叶石楠进行移植,植物移植后立即进水,使水面接近于湿地表层土壤,1周后湿地植物开始恢复生长,从而让移植植物适应人工湿地系统的环境并生长和湿地床内基质表面的挂膜。The constructed wetlands are transplanted with wild rice stems, pikegrass, ryegrass and Photinia frondosa. Immediately after the plants are transplanted, they are flooded with water so that the water surface is close to the surface soil of the wetland. The wetland plants begin to grow again one week later, so that the transplanted plants can adapt to the conditions of the constructed wetland system. Environment and growth and hanging film on the surface of the substrate in the wetland bed.

利用上述人工湿地系统处理尾水的运行方式如下:人工湿地的启动完毕后,对多级填料人工湿地系统深度净化污水处理厂尾水效果进行监测,具体操作为:采用运行模式为进水-处理24h-排空的人工湿地系统对污水处理厂尾水进行深度净化。The operation mode of using the above-mentioned constructed wetland system to treat tail water is as follows: After the construction of the constructed wetland is completed, the effect of the deep purification of the tail water of the sewage treatment plant in the multi-stage filler constructed wetland system is monitored. The specific operation is: the operation mode is water inflow-treatment The 24h-empty artificial wetland system performs deep purification of the tail water of the sewage treatment plant.

以下提供4个实施例进一步说明人工湿地的稳定运行情况。实施例用于说明本发明内容,而不是限定本发明内容。Four examples are provided below to further illustrate the stable operation of the constructed wetland. The examples are used to illustrate the contents of the present invention, not to limit the contents of the present invention.

实施例1Example 1

如附图1、附图2及附图3所示,处理尾水量12m3/d的多级填料潜流式人工湿地整体规格为L×B×H=15.96m×3.74m×2.00m,其分为5个区域,沿尾水水流方向依次构建长度为L1=1.0m的集水池I、长度为L2=1.0m的配水槽II、长度为L3=10m的湿地床体区III、长度为L4=1.0m的沉淀区IV与长度为L5=1.0m的清水池V,其整体由三七墙砖砌而成,其中配水槽与沉淀区分别用二四墙砖砌布水墙隔开(墙上布有间距为300mm的孔径为20mm的小孔)。湿地床体区依次填充厚度为H1=26cm的粒径40-50mm砾石、厚度为H2=52cm的粒径20-40mm红砖碎块、厚度为H3=39cm的粒径8-10mm钢渣、厚度为H4=32cm的粒径4-8mm陶粒和厚度为H5=51cm的粘土层(每层用网格1mm×1mm的纱网隔开)来构建湿地填料(湿地填料孔隙率为30.15%),床底坡度1%。湿地系统栽种茭白、梭鱼草、黑麦草与红叶石楠,并且安装拔风管3。污水处理厂尾水经水管收集通过调节阀门引入集水池汇集后,经溢流堰1溢流进入在配水槽内,再经其后端布水墙2对尾水进行均质均量,进入湿地床体区联合物理、化学、生物方法对尾水进行深度净化处理,其后处理水自流通过布水墙均质均量来到沉淀区沉淀去除大颗粒杂质,再经溢流堰溢流汇集于清水池,控制阀门将处理后的尾水外排。As shown in attached drawing 1, attached drawing 2 and attached drawing 3, the overall specification of the multi-stage packing subsurface flow constructed wetland with a tail water treatment volume of 12m 3 /d is L×B×H=15.96m×3.74m×2.00m, and its There are 5 areas, and along the direction of the tail water flow, a sump I with a length of L1 = 1.0m, a water distribution channel II with a length of L2 = 1.0m, a wetland bed area III with a length of L3 = 10m, and a length of L4 = The 1.0m sedimentation area IV and the clear water pool V with a length of L5 = 1.0m are made of three-seven-wall bricks as a whole, and the water distribution tank and the sedimentation area are separated by two or four brick water distribution walls (walls There are small holes with a hole diameter of 20mm at a distance of 300mm). The wetland bed area is sequentially filled with gravel with a particle size of 40-50 mm and a thickness of H1 = 26 cm, red brick fragments with a particle size of 20-40 mm and a thickness of H2 = 52 cm, steel slag with a particle size of 8-10 mm and a thickness of H3 = 39 cm, and a thickness of H4=32cm ceramsite with a particle size of 4-8mm and a clay layer with a thickness of H5=51cm (each layer is separated by a gauze mesh of 1mm×1mm) to construct the wetland filler (the porosity of the wetland filler is 30.15%), the bed The bottom slope is 1%. Water bamboo, barracuda, ryegrass and Photinia are planted in the wetland system, and the wind pipe 3 is installed. The tail water of the sewage treatment plant is collected through the water pipe and introduced into the sump through the regulating valve. After being collected, it overflows through the overflow weir 1 and enters the water distribution tank, and then the tail water is homogenized and equalized by the water distribution wall 2 at the rear end, and enters the wetland. The bed area combines physical, chemical, and biological methods to carry out deep purification treatment of tail water, and then the treated water flows through the water distribution wall to the sedimentation area to precipitate and remove large particles of impurities, and then overflows through the overflow weir and collects in the In the clear water tank, the control valve discharges the treated tail water.

实施例2Example 2

如附图1、附图2及附图3所示,处理尾水量21m3/d的多级填料潜流式人工湿地整体规格为L×B×H=17.96m×5.24m×2.00m,其分为5个区域,沿尾水水流方向依次构建长度为L1=1.0m的集水池I、长度为L2=1.0m的配水槽II、长度为L3=12m的湿地床体区III、长度为L4=1.0m的沉淀区IV与长度为L5=1.0m的清水池V,其整体由三七墙砖砌而成,其中配水槽与沉淀区分别用二四砖砌布水墙隔开(墙上布有间距为300mm的孔径为20mm的小孔)。湿地床体区依次填充厚度为H1=26cm的粒径40-50mm砾石、厚度为H2=52cm的粒径20-40mm红砖碎块、厚度为H3=39cm的粒径8-10mm钢渣、厚度为H4=32cm的粒径4-8mm陶粒和厚度为H5=51cm的粘土层(每层用网格1mm×1mm的纱网隔开)来构建湿地填料(湿地填料孔隙率为34.51%),床底坡度1%。湿地系统栽种茭白、梭鱼草、黑麦草与红叶石楠,并且安装拔风管3。污水处理厂尾水经水管收集通过调节阀门引入集水池汇集后,经溢流堰1溢流进入在配水槽内,再经其后端布水墙2对尾水进行均质均量,进入湿地床体区联合物理、化学、生物方法对尾水进行深度净化处理,其后处理水自流通过布水墙均质均量来到沉淀区沉淀去除大颗粒杂质,再经溢流堰溢流汇集于清水池,控制阀门将处理后的尾水外排。As shown in attached drawing 1, attached drawing 2 and attached drawing 3, the overall specification of the subsurface flow constructed wetland with multi-stage packing with a treatment tail water volume of 21m 3 /d is L×B×H=17.96m×5.24m×2.00m, which is divided into There are 5 areas, and along the direction of the tail water flow, a sump I with a length of L1 = 1.0m, a water distribution channel II with a length of L2 = 1.0m, a wetland bed area III with a length of L3 = 12m, and a length of L4 = The 1.0m sedimentation area IV and the clear water pool V with a length of L5 = 1.0m are made of three-seven-wall bricks as a whole, and the water distribution tank and the sedimentation area are separated by two or four brick water walls (wall cloth There are small holes with a hole diameter of 20mm at a distance of 300mm). The wetland bed area is sequentially filled with gravel with a particle size of 40-50 mm and a thickness of H1 = 26 cm, red brick fragments with a particle size of 20-40 mm and a thickness of H2 = 52 cm, steel slag with a particle size of 8-10 mm and a thickness of H3 = 39 cm, and a thickness of H4=32cm ceramsite with a particle size of 4-8mm and a clay layer with a thickness of H5=51cm (each layer is separated by a gauze mesh of 1mm×1mm) to construct the wetland filler (the porosity of the wetland filler is 34.51%), the bed The bottom slope is 1%. Water bamboo, barracuda, ryegrass and Photinia are planted in the wetland system, and the wind pipe 3 is installed. The tail water of the sewage treatment plant is collected through the water pipe and introduced into the sump through the regulating valve. After being collected, it overflows through the overflow weir 1 and enters the water distribution tank, and then the tail water is homogenized and equalized through the water distribution wall 2 at the rear end, and enters the wetland. The bed area combines physical, chemical, and biological methods to carry out deep purification treatment of tail water, and then the treated water flows through the water distribution wall to the sedimentation area to precipitate and remove large particles of impurities, and then overflows through the overflow weir and collects in the In the clear water tank, the control valve discharges the treated tail water.

实施例3Example 3

如附图1、附图2及附图3所示,处理尾水量56m3/d的多级填料潜流式人工湿地整体规格为L×B×H=26.96m×4.74m×2.00m,其分为5个区域,沿尾水水流方向依次构建长度为L1=1.0m的集水池I、长度为L2=1.0m的配水槽II、长度为L3=21m的湿地床体区III、长度为L4=1.0m的沉淀区IV与长度为L5=1.0m的清水池V,其整体由三七墙砖砌而成,其中配水槽与沉淀区分别用二四砖砌布水墙隔开(墙上布有间距为300mm的孔径为20mm的小孔)。湿地床体区依次填充厚度为H1=26cm的粒径40-50mm砾石、厚度为H2=52cm的粒径20-40mm红砖碎块、厚度为H3=39cm的粒径8-10mm钢渣、厚度为H4=32cm的粒径4-8mm陶粒和厚度为H5=51cm的粘土层(每层用网格1mm×1mm的纱网隔开)来构建湿地填料(湿地填料孔隙率为33.46%),床底坡度1%。湿地系统栽种茭白、梭鱼草、黑麦草与红叶石楠,并且安装拔风管3。污水处理厂尾水经水管收集通过调节阀门引入集水池汇集后,经溢流堰1溢流进入在配水槽内,再经其后端布水墙2对尾水进行均质均量,进入湿地床体区联合物理、化学、生物方法对尾水进行深度净化处理,其后处理水自流通过布水墙均质均量来到沉淀区沉淀去除大颗粒杂质,再经溢流堰溢流汇集于清水池,控制阀门将处理后的尾水外排。As shown in attached drawing 1, attached drawing 2 and attached drawing 3, the overall specification of the subsurface flow constructed wetland with multi-stage packing with a treatment tail water volume of 56m 3 /d is L×B×H=26.96m×4.74m×2.00m, which is divided into There are 5 areas, and along the direction of the tail water flow, a sump I with a length of L1=1.0m, a water distribution channel II with a length of L2=1.0m, a wetland bed area III with a length of L3=21m, and a length of L4= The 1.0m sedimentation area IV and the clear water pool V with a length of L5 = 1.0m are made of three-seven-wall bricks as a whole, and the water distribution tank and the sedimentation area are separated by two or four brick water walls (wall cloth There are small holes with a hole diameter of 20mm at a distance of 300mm). The wetland bed area is sequentially filled with gravel with a particle size of 40-50 mm and a thickness of H1 = 26 cm, red brick fragments with a particle size of 20-40 mm and a thickness of H2 = 52 cm, steel slag with a particle size of 8-10 mm and a thickness of H3 = 39 cm, and a thickness of H4=32cm ceramsite with a particle size of 4-8mm and a clay layer with a thickness of H5=51cm (each layer is separated by a mesh of 1mm×1mm gauze) to construct the wetland filler (the porosity of the wetland filler is 33.46%), the bed The bottom slope is 1%. Water bamboo, barracuda, ryegrass and Photinia are planted in the wetland system, and the wind pipe 3 is installed. The tail water of the sewage treatment plant is collected through the water pipe and introduced into the sump through the regulating valve. After being collected, it overflows through the overflow weir 1 and enters the water distribution tank, and then the tail water is homogenized and equalized by the water distribution wall 2 at the rear end, and enters the wetland. The bed area combines physical, chemical, and biological methods to carry out deep purification treatment of tail water, and then the treated water flows through the water distribution wall to the sedimentation area to precipitate and remove large particles of impurities, and then overflows through the overflow weir and collects in the In the clear water tank, the control valve discharges the treated tail water.

实施例4Example 4

如附图1、附图2及附图3所示,处理尾水量84m3/d的多级填料潜流式人工湿地整体规格为L×B×H=26.96m×6.74m×2.00m,其分为5个区域,沿尾水水流方向依次构建长度为L1=1.0m的集水池I、长度为L2=1.0m的配水槽II、长度为L3=21m的湿地床体区III、长度为L4=1.0m的沉淀区IV与长度为L5=1.0m的清水池V,其整体由三七墙砖砌而成,其中配水槽与沉淀区分别用二四墙砖砌布水墙隔开(墙上布有间距为300mm的孔径为20mm的小孔)。湿地床体区依次填充厚度为H1=26cm的粒径40-50mm砾石、厚度为H2=52cm的粒径20-40mm红砖碎块、厚度为H3=39cm的粒径8-10mm钢渣、厚度为H4=32cm的粒径4-8mm陶粒和厚度为H5=51cm的粘土层(每层用网格1mm×1mm的纱网隔开)来构建湿地填料(湿地填料孔隙率为33.12%),床底坡度1%。湿地系统栽种茭白、梭鱼草、黑麦草与红叶石楠,并且安装拔风管3。污水处理厂尾水经水管收集通过调节阀门引入集水池汇集后,经溢流堰1溢流进入在配水槽内,再经其后端布水墙2对尾水进行均质均量,进入湿地床体区联合物理、化学、生物方法对尾水进行深度净化处理,其后处理水自流通过布水墙均质均量来到沉淀区沉淀去除大颗粒杂质,再经溢流堰溢流汇集于清水池,控制阀门将处理后的尾水外排。As shown in attached drawing 1, attached drawing 2 and attached drawing 3, the overall specification of the subsurface flow constructed wetland with multi-stage packing with a tail water treatment volume of 84m 3 /d is L×B×H=26.96m×6.74m×2.00m, which is divided into There are 5 areas, and along the direction of the tail water flow, a sump I with a length of L1=1.0m, a water distribution channel II with a length of L2=1.0m, a wetland bed area III with a length of L3=21m, and a length of L4= The 1.0m sedimentation area IV and the clear water pool V with a length of L5 = 1.0m are made of three-seven-wall bricks as a whole, and the water distribution tank and the sedimentation area are separated by two or four brick water distribution walls (walls There are small holes with a hole diameter of 20mm at a distance of 300mm). The wetland bed area is sequentially filled with gravel with a particle size of 40-50 mm and a thickness of H1 = 26 cm, red brick fragments with a particle size of 20-40 mm and a thickness of H2 = 52 cm, steel slag with a particle size of 8-10 mm and a thickness of H3 = 39 cm, and a thickness of H4=32cm ceramsite with a particle size of 4-8mm and a clay layer with a thickness of H5=51cm (each layer is separated by a gauze mesh of 1mm×1mm) to construct the wetland filler (the porosity of the wetland filler is 33.12%), the bed The bottom slope is 1%. Water bamboo, barracuda, ryegrass and Photinia are planted in the wetland system, and the wind pipe 3 is installed. The tail water of the sewage treatment plant is collected through the water pipe and introduced into the sump through the regulating valve. After being collected, it overflows through the overflow weir 1 and enters the water distribution tank, and then the tail water is homogenized and equalized by the water distribution wall 2 at the rear end, and enters the wetland. The bed area combines physical, chemical, and biological methods to carry out deep purification treatment of tail water, and then the treated water flows through the water distribution wall to the sedimentation area to precipitate and remove large particles of impurities, and then overflows through the overflow weir and collects in the In the clear water tank, the control valve discharges the treated tail water.

Claims (1)

1. a multistage packing artificial wetland method of construction, comprises the construction of artificial swamp structure, thin portion, wetland bed tagma builds, pond body surrounding pool wall is built, it is characterized in that:
Described artificial swamp structure is built: overall specification is long × wide × dark (L × B × H), be divided into 5 regions, water collecting basin, distributing trough, wetland bed tagma, settling region and clean water basin are built successively along tail water water (flow) direction, its entirety is built by pseudo-ginseng wall brick and is formed, and wherein distributing trough and settling region separate (wall is furnished with aperture) with two or four brick cloth waterwalls respectively.Sewage treatment plant tail water is after water pipe collecting is collected by regulated valve introducing water collecting basin, enter in distributing trough through overflow weir overflow, carry out homogeneous through its rear end cloth waterwall to tail water more all to measure, enter and the wetland bed tagma associating physics, chemistry, the biological method that pull out airduct are housed deep purifying process is carried out to tail water, its aftertreatment water from flow through water distribution wall homogeneous all measure come settling region precipitation remove large granular impurity, come together in clean water basin through overflow weir overflow again, the tail water after process is arranged outward by by-pass valve control.
Thin portion, described wetland bed tagma builds: particle diameter 40-50mm gravel is filled in wetland bed tagma successively, particle diameter 20-40mm common brick fragment, particle diameter 8-10mm slag, particle diameter 4-8mm haydite, clay seam (every layer separates with the gauze of grid 1mm × 1mm) build wet land filler, bed bottom sloping 1%.Wetland bed collocation plantation wild rice stem, photinia glabra, mullet grass and rye grass, and be mounted with and pull out airduct.Artificial swamp selects the wild rice stem in vegetative period, mullet grass, rye grass and photinia glabra to transplant in the present invention, intake immediately after plant transplanting, make the water surface close to wetland topsoil, after 1 week, wetland plant starts restoration ecosystem, thus allows the environment transplanting plant adaptation artificial wet land system also grow and wetland bed biofilm.
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CN101293708A (en) * 2007-04-25 2008-10-29 宝山钢铁股份有限公司 A Constructed Wetland and Its Application
CN101851023A (en) * 2010-03-26 2010-10-06 北京神州瑞霖环保科技有限公司 A coke powder-steel slag composite filler subsurface flow constructed wetland system

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CN107777782A (en) * 2017-11-13 2018-03-09 中国地质科学院水文地质环境地质研究所 Contaminated land spring Water quality restoration conservation integral device
CN107777782B (en) * 2017-11-13 2020-04-07 中国地质科学院水文地质环境地质研究所 Water quality restoration and conservation integrated device for polluted surface spring
CN108658235A (en) * 2017-12-11 2018-10-16 北京林业大学 Drowned flow artificial wet land, its construction method and the sewage water denitrification handling method of sewage water denitrification processing
CN115893669A (en) * 2021-09-22 2023-04-04 西南湿地有限公司 Vertical flow constructed wetland packed bed construction method for efficiently removing various pollutants
CN119306338A (en) * 2023-07-13 2025-01-14 中国石油化工股份有限公司 A system and method for treating oily fractured sewage

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Application publication date: 20160302