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CN103288215A - Anti-seepage constructed wetland system - Google Patents

Anti-seepage constructed wetland system Download PDF

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CN103288215A
CN103288215A CN2013101594074A CN201310159407A CN103288215A CN 103288215 A CN103288215 A CN 103288215A CN 2013101594074 A CN2013101594074 A CN 2013101594074A CN 201310159407 A CN201310159407 A CN 201310159407A CN 103288215 A CN103288215 A CN 103288215A
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seepage
air
water
sewage
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CN103288215B (en
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刘黾
陈章和
许冲勇
廖秋成
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South Of Five Ridges Ecological Culture Brigade Ltd By Share Ltd
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LINGNAN LANDSCAPE CO Ltd
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    • 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
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    • Y02W10/10Biological treatment of water, waste water, or sewage

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Abstract

The invention provides an anti-seepage artificial wetland system which comprises an artificial wetland pool, wherein the bottom and the periphery of the artificial wetland pool are provided with anti-seepage layers, the artificial wetland pool is sequentially provided with a planting layer, a gravel layer, a composite filler layer and a drain pipe, wherein wetland plants are planted in the planting layer, the planting layer is used for primarily purifying sewage, the gravel layer is used for secondarily purifying the sewage, the composite filler layer is used for secondarily purifying the sewage, and the drain pipe is arranged from top to bottom, and the anti-seepage layers are made of 0.06-0.07 part of water-soluble silicon dioxide, 0.08-0.1 part of potassium methyl silicate, 0.4-0.5 part of potassium silicate, 260-1800 parts of river sand and 70-220 parts of water. The sewage is purified in a triple mode through the planting layer, the gravel layer and the composite packing layer, and the purification efficiency is improved; the anti-seepage layer made of different formulas is selected, so that the anti-aging and high and low temperature resistance of the anti-seepage layer of the artificial wetland is greatly improved, and the anti-seepage capability of the artificial wetland system is improved.

Description

一种防渗人工湿地系统An anti-seepage constructed wetland system

技术领域 technical field

本发明涉及人工湿地营建与水土涵养领域,具体涉及一种防渗人工湿地系统,尤其适用于垂直流的人工湿地系统。  The invention relates to the fields of artificial wetland construction and water and soil conservation, in particular to an anti-seepage artificial wetland system, especially suitable for vertical flow artificial wetland systems. the

背景技术 Background technique

人工湿地的研究起源于20世纪70年代,是在研究湿地的基础上衍生出来的。人工湿地是由人工建造和控制运行的与沼泽地类似的地面,将污水、污泥有控制的投配到经人工建造的湿地上,污水与污泥在沿一定方向流动的过程中,主要利用土壤、人工介质、植物、微生物的物理、化学、生物三重协同作用,对污水、污泥进行处理的一种技术。其作用机理包括吸附、滞留、过滤、氧化还原、沉淀、微生物分解、转化、植物遮蔽、残留物积累、蒸腾水分和养分吸收及各类动物的作用。人工湿地由于具有投资低、耗能少、缓冲容量大、工艺简单等特点,已被广泛用于生活污水、暴雨径流、农村面源污染及湖泊污染防治。  The study of constructed wetlands originated in the 1970s and was derived from the study of wetlands. Constructed wetland is a ground similar to swampland that is artificially constructed and operated under control. Sewage and sludge are distributed to the artificially constructed wetland in a controlled manner. When sewage and sludge flow in a certain direction, they are mainly used It is a technology for treating sewage and sludge through the triple synergy of physics, chemistry and biology of soil, artificial medium, plants and microorganisms. Its mechanism of action includes adsorption, retention, filtration, redox, precipitation, microbial decomposition, transformation, plant shading, residue accumulation, transpiration of water and nutrient absorption, and the action of various animals. Due to the characteristics of low investment, low energy consumption, large buffer capacity, and simple process, constructed wetlands have been widely used for domestic sewage, storm runoff, rural non-point source pollution and lake pollution prevention and control. the

人工湿地主要包括水平流人工湿地和垂直流人工湿地两种。水平流人工湿地是使污水由进水口一端沿水平方向流动的过程中依次通过砂石、介质、植物根系,流向出水口一端,以达到净化目的。水平流人工湿地水位较浅,运行受自然气候条件影响较大,易生蚊蝇,并有异味。在垂直流人工湿地系统中,污水由表面纵向流至床底,在纵向流的过程中污水依次经过不同的介质层,达到净化的目的。垂直流人工湿地较水平流人工湿地,独特的构筑结构和水流模式,使其具有占地面积小、处理效率高、无恶臭等优点,逐渐成为人工湿地系统的主流。  Constructed wetlands mainly include horizontal flow constructed wetlands and vertical flow constructed wetlands. The horizontal flow constructed wetland is to make the sewage flow through the sand, medium, and plant roots in the process of flowing horizontally from the water inlet to the water outlet to achieve the purpose of purification. The water level of the horizontal flow artificial wetland is relatively shallow, and its operation is greatly affected by natural climate conditions, which are prone to mosquitoes and flies, and have peculiar smell. In the vertical flow constructed wetland system, the sewage flows vertically from the surface to the bottom of the bed, and in the process of vertical flow, the sewage passes through different medium layers successively to achieve the purpose of purification. Compared with horizontal flow constructed wetlands, vertical flow constructed wetlands have the advantages of small footprint, high treatment efficiency, and no odor due to their unique construction structure and water flow pattern, and have gradually become the mainstream of constructed wetland systems. the

垂直流人工系统由于水位较深,产生压强大,故对于人工湿地池的防渗技术提出较高要求。目前设置在人工湿地池底部和侧壁上的防渗材料存在着易老化、受高低温影响大以及价格昂贵的不足,大大减低了人工湿地处理污水的效率。另外,垂直流人工湿地由于其垂直结构,使得湿地内供氧不足,将整个系统置于相对单一的厌氧环境,使得顶部好氧区的硝化反应受抑制,氮的去除率降低;为了提高湿地内部的供氧效果,目前的人工湿地普遍采用底部曝气的增 氧方式,但垂直流人工湿地底部为厌氧区域,底部曝气方式将使得人工湿地底部厌氧区过小,影响系统内的反硝化反应。  Due to the deep water level and strong pressure generated by the vertical flow artificial system, higher requirements are put forward for the anti-seepage technology of the constructed wetland pool. At present, the anti-seepage materials installed on the bottom and side walls of the constructed wetland pool have the disadvantages of easy aging, great influence of high and low temperature, and high price, which greatly reduces the efficiency of sewage treatment in the constructed wetland. In addition, due to its vertical structure, the vertical flow artificial wetland makes the oxygen supply in the wetland insufficient, and the whole system is placed in a relatively single anaerobic environment, which inhibits the nitrification reaction in the top aerobic zone and reduces the nitrogen removal rate; in order to improve the wetland For the internal oxygen supply effect, the current artificial wetland generally adopts the method of increasing oxygen by bottom aeration, but the bottom of the vertical flow constructed wetland is an anaerobic area, and the bottom aeration method will make the anaerobic area at the bottom of the constructed wetland too small, which will affect the oxygen in the system. denitrification reaction. the

发明内容 Contents of the invention

本发明的目的是克服现有技术中的不足之处,提供一种污水处理效率高的防渗人工湿地系统。  The purpose of the present invention is to overcome the deficiencies in the prior art and provide an anti-seepage artificial wetland system with high sewage treatment efficiency. the

本发明的目的是通过以下技术方案来实现的:  The purpose of the present invention is achieved by the following technical solutions:

一种防渗人工湿地系统,包括底部和四周均设置有防渗层的人工湿地池,所述人工湿地池由上至下依次设置栽植有湿地植物并用于对污水进行初次净化的种植层、用于对污水进行二次净化的砾石层、用于对污水进行再次净化的复合填料层以及排水管,所述防渗层由如下质量份的物质制成:  An anti-seepage constructed wetland system, including a constructed wetland pool with anti-seepage layers on the bottom and surroundings, the constructed wetland pool is sequentially provided with planting layers planted with wetland plants and used for primary purification of sewage. For the gravel layer for secondary purification of sewage, the composite packing layer for secondary purification of sewage, and the drainage pipe, the anti-seepage layer is made of the following mass parts:

水溶性二氧化硅,0.06~0.07份;  Water-soluble silica, 0.06-0.07 parts;

甲基硅酸钾,0.08~0.1份;  Potassium methyl silicate, 0.08-0.1 part;

硅酸钾,0.4~0.5份;  Potassium silicate, 0.4-0.5 parts;

河沙,260份~1800份;  River sand, 260-1800 parts;

以及水,70~220份。  And water, 70~220 parts. the

制成防渗层的组成物质,分别具有如下特性:  The constituent materials of the anti-seepage layer have the following characteristics:

水溶性二氧化硅,成化学惰性,用于抗结剂;  Water-soluble silica, chemically inert, used as anti-caking agent;

甲基硅酸钾,具有可渗透、可吸收,且能够保持基底的自然外表的特性,可与空气中的CO2或其他酸性化合物反应,在基材表层形成一层不能溶解的网状防水透气膜,具有优秀的防水效果和防渗、防潮、阻锈、抗老化、抗污染等优点,避免水分吸入基底,从而减少冻融和风化引起的剥落,增加基底寿命;  Potassium methyl silicate, which is permeable, absorbable, and able to maintain the natural appearance of the substrate, can react with CO2 or other acidic compounds in the air to form an insoluble mesh waterproof and breathable film on the surface of the substrate , has excellent waterproof effect and anti-seepage, moisture-proof, anti-rust, anti-aging, anti-pollution and other advantages, avoiding moisture absorption into the substrate, thereby reducing peeling caused by freeze-thawing and weathering, and increasing the life of the substrate; 

硅酸钾,用于提高防渗层表面的耐温能力,同时防止防渗层表面结晶;  Potassium silicate, used to improve the temperature resistance of the surface of the anti-seepage layer and prevent crystallization of the surface of the anti-seepage layer;

河沙,在防渗层中起骨架或填充作用;  River sand, which plays a skeleton or filling role in the anti-seepage layer;

上述方案中,通过利用水溶性二氧化硅、甲基硅酸钾、硅酸钾、河沙以及水制成的防渗层极大提高了防渗层耐老化、耐高低温性能,从而提高防渗能力,同时制备防渗层的物质均为常见物质,极易得到,且价格便宜。  In the above scheme, the anti-seepage layer made of water-soluble silica, potassium methyl silicate, potassium silicate, river sand and water has greatly improved the aging resistance and high and low temperature resistance of the anti-seepage layer, thereby improving the anti-seepage performance. In addition, the materials used to prepare the anti-seepage layer are all common materials, which are easy to obtain and cheap. the

所述人工湿地池的形状可以为任一规则图形,优选为长方形;具体的,长方形人工湿地池的长宽比为5:1~10:1,深度为100cm~140cm。  The shape of the constructed wetland pool can be any regular figure, preferably rectangular; specifically, the aspect ratio of the rectangular constructed wetland pool is 5:1-10:1, and the depth is 100cm-140cm. the

所述种植层上覆盖有污泥,便于湿地植物的生长和附着,作为优选技术方案,污泥的厚度为20cm~30cm;种植层上种植的湿地植物可以为方便在湿地环境生长的水生植物,如芦苇、美人蕉、菖蒲等,也可以为成活率高、根系发达、生长周期长的挺水植物,例如水葫芦,水葱等。  The planting layer is covered with sludge to facilitate the growth and attachment of wetland plants. As a preferred technical solution, the thickness of the sludge is 20cm to 30cm; the wetland plants planted on the planting layer can be aquatic plants that are convenient for growing in a wetland environment. Such as reed, canna, calamus, etc., can also be emergent plants with high survival rate, well-developed root system, and long growth cycle, such as water hyacinth and water onion. the

所述砾石层通过过滤对大颗粒杂质进行阻挡迂回,并利用其表面微生物的物理、化学和生化反应联合作用去除被过滤的大颗粒杂质,对污水进行二次净化。  The gravel layer blocks large particles of impurities through filtration, and uses the combined action of physical, chemical and biochemical reactions of microorganisms on the surface to remove the filtered large particles of impurities to perform secondary purification of sewage. the

所述复合填料层,用于对砾石层净化后的污水进行再次净化;发明人通过长期研究发现,复合填料层在孔隙率≥30%、体积密度为1200~1500Kg/m3、透水速率为15~20m/h的条件下,对污水的净化效果最好。其中:  The composite packing layer is used to purify the sewage after the gravel layer is purified; the inventor has found through long-term research that the composite packing layer has a porosity ≥ 30%, a bulk density of 1200-1500Kg/m 3 , and a water permeability of 15 Under the condition of ~20m/h, the purification effect on sewage is the best. in:

孔隙率,指散粒状材料堆积体积中,颗粒之间的空隙体积占总体积的比例;  Porosity refers to the ratio of the void volume between particles to the total volume in the bulk volume of granular materials;

体积密度,指包括材料体积内所有孔在内的表观密度;  Bulk density means the apparent density including all pores in the volume of the material;

透水速率,指水在过滤材料内部结构的流动速度。  The water permeability rate refers to the flow rate of water in the internal structure of the filter material. the

为了提高复合材料层的净化效果,作为进一步改进技术方案,所述复合填料层由如下质量比的物质制成:  In order to improve the purification effect of the composite material layer, as a further technical solution for improvement, the composite filler layer is made of substances with the following mass ratios:

粒径为2~8mm的石灰石,10-20%;  Limestone with a particle size of 2-8mm, 10-20%;

粒径为3~10mm的煤渣,20-30%;  Cinder with a particle size of 3-10mm, 20-30%;

粒径小于2mm的粉煤灰,5-10%;  Fly ash with particle size less than 2mm, 5-10%;

粒径小于2mm的粘土,15-20%;  Clay with particle size less than 2mm, 15-20%;

粒径为3~8mm火山岩,5-20%;  Volcanic rock with a particle size of 3-8mm, 5-20%;

粒径为2~8mm改性硅藻土,5-10%;  Modified diatomite with a particle size of 2-8mm, 5-10%;

以及水,5-10%。  and water, 5-10%. the

作为进一步改进技术方案,所述防渗人工湿地系统还包括一供气装置,供气装置的供气管横插于所述人工湿地池的中上部且位于砾石层内,所述供气管的上表面均匀设置有多个供气孔,供气孔覆盖有匹配的保护片,所述保护片与供气管为活动连接,使保护片在供气时被掀起,在不供气时复位。  As a further improved technical solution, the anti-seepage constructed wetland system also includes an air supply device, the air supply pipe of the air supply device is inserted in the middle and upper part of the constructed wetland pool and is located in the gravel layer, and the upper surface of the air supply pipe A plurality of air supply holes are evenly arranged, and the air supply holes are covered with a matching protective sheet, and the protective sheet is movably connected with the air supply pipe, so that the protective sheet is lifted when the air is supplied, and resets when the air is not supplied. the

作为更进一步改进技术方案,所述供气装置还包括与供气管连接的空气压缩机,所述供气管外套有保护性的硬质透气网管,为了防止所处砾石层内的填料穿透透气网管损坏供气管,所述透气网管的网格直径小于所处砾石层填料的粒径。  As a further improved technical solution, the air supply device also includes an air compressor connected to the air supply pipe, and the air supply pipe is covered with a protective hard air-permeable mesh pipe, in order to prevent the filler in the gravel layer from penetrating the air-permeable mesh pipe The air supply pipe is damaged, and the mesh diameter of the breathable mesh pipe is smaller than the particle diameter of the gravel layer filler where it is located. the

本发明相比现有技术具有以下优点及有益效果:  Compared with the prior art, the present invention has the following advantages and beneficial effects:

(1)本发明通过种植层、砾石层以及复合填料层对污水进行三重净化,提高了净化的效率,而复合填料层的结构及制备成分进一步提高了本发明人工湿地的净化效率;  (1) The present invention performs triple purification of sewage through the planting layer, gravel layer and composite packing layer, which improves the purification efficiency, and the structure and preparation components of the composite packing layer further improve the purification efficiency of the constructed wetland of the present invention;

(2)本发明通过选用不同配方制成的防渗层,极大提高了人工湿地防渗层耐老化、耐高低温性能,从而提高防渗能力;同时,制备防渗层的物质均为常见物质,极易得到,且价格便宜;  (2) The present invention greatly improves the anti-seepage performance of the artificial wetland anti-seepage layer by selecting the anti-seepage layer made of different formulas, thereby improving the anti-seepage ability; at the same time, the materials used to prepare the anti-seepage layer are common Substances are easily available and cheap;

(3)本发明通过在人工湿地池中上部设置供气管,且供气孔设置在供气管的上表面,促进了人工湿地池顶部好氧区的硝化反应,以及人工湿地池底部厌氧区的反硝化反应,从而提高了人工湿地的净化能力;  (3) The present invention promotes the nitrification reaction in the aerobic zone at the top of the constructed wetland pool and the reaction in the anaerobic zone at the bottom of the constructed wetland pool by setting an air supply pipe in the middle and upper part of the constructed wetland pool, and the air supply holes are arranged on the upper surface of the air supply pipe. Nitrification reaction, thereby improving the purification capacity of constructed wetlands;

(4)本发明通过在供气孔覆盖匹配的保护片,保护片与供气管为活动连接,使保护片在供气时被掀起,在不供气时复位,这种结构避免供气孔被污水里的杂质堵塞而阻止供气管正常供气;  (4) In the present invention, by covering the air supply hole with a matching protective sheet, the protective sheet is movably connected with the air supply pipe, so that the protective sheet is lifted when the air is supplied and reset when the air is not supplied. This structure prevents the air supply hole from being polluted by sewage. Impurities block the air supply pipe to prevent normal air supply;

(5)本发明通过在供气管外部套装硬质透气网管,且透气网管的网格直径小于所处砾石层填料的粒径,提高了对供气管的保护;  (5) The present invention improves the protection of the air supply pipe by installing a hard breathable mesh pipe outside the air supply pipe, and the mesh diameter of the breathable mesh pipe is smaller than the particle size of the gravel layer filler;

(6)本发明提供的防渗人工湿地系统的结构简单,易实现。  (6) The anti-seepage constructed wetland system provided by the present invention has a simple structure and is easy to realize. the

附图说明 Description of drawings

图1为本发明防渗人工湿地系统结构示意图。  Fig. 1 is a schematic diagram of the structure of the anti-seepage constructed wetland system of the present invention. the

具体实施方式 Detailed ways

下面结合实施例及附图对本发明作进一步详细的描述,但本发明创造的实施方式不限于此。  The present invention will be further described in detail below with reference to the embodiments and the accompanying drawings, but the embodiments of the present invention are not limited thereto. the

如图1所示,本发明提供的一种防渗人工湿地系统,包括底部和四周均设置有防渗层5的长方形人工湿地池,人工湿地池由上至下依次设置栽植有湿地植物并用于对污水进行初次净化的种植层1、用于对污水进行二次净化的砾石层2、用于对污水进行再次净化的复合填料层3以及排水管4;防渗人工湿地系统还包括一供气装置,供气装置包括供气管6、与供气管6连接的空气压缩机8以及外套在供气管6上的硬质透气网管7,供气管6横插于人工湿地池的中上部且位于砾石层2内,供气管2的上表面均匀设置有多个供气孔,供气孔覆盖有匹配的保护 片,保护片与供气管为活动连接,使保护片在供气时被掀起,在不供气时复位,透气网管7的网格直径小于所处砾石层2填料的粒径。  As shown in Figure 1, an anti-seepage constructed wetland system provided by the present invention includes a rectangular constructed wetland pool provided with an anti-seepage layer 5 at the bottom and surroundings, and the constructed wetland pool is sequentially arranged with wetland plants from top to bottom for Planting layer 1 for primary purification of sewage, gravel layer 2 for secondary purification of sewage, composite packing layer 3 for secondary purification of sewage, and drainage pipe 4; the anti-seepage constructed wetland system also includes a gas supply The air supply device includes an air supply pipe 6, an air compressor 8 connected to the air supply pipe 6, and a hard breathable mesh pipe 7 covered on the air supply pipe 6. The air supply pipe 6 is inserted horizontally in the middle and upper part of the constructed wetland pool and is located in the gravel layer. In 2, the upper surface of the air supply pipe 2 is uniformly provided with a plurality of air supply holes, and the air supply holes are covered with a matching protective sheet. The protective sheet is movably connected with the air supply pipe, so that the protective sheet is lifted when the air is supplied, and when it is not supplied. Reset, the mesh diameter of the air-permeable mesh pipe 7 is smaller than the particle diameter of the filler in the gravel layer 2 . the

其中:  in:

防渗层材料采取以下方法制成:  The anti-seepage layer material is made by the following methods:

(1)将0.06~0.07份的水溶性二氧化硅、0.08~0.1份的甲基硅酸钾、0.4~0.5份的硅酸钾以及0.6份的水配制成疏水剂;  (1) Mix 0.06-0.07 parts of water-soluble silicon dioxide, 0.08-0.1 parts of potassium methyl silicate, 0.4-0.5 parts of potassium silicate and 0.6 parts of water to make a hydrophobic agent;

(2)将(1)中配制的疏水剂与水按照质量比为1:70~1:220的比例配制成疏水溶液;  (2) Prepare the hydrophobic agent prepared in (1) and water according to the mass ratio of 1:70 to 1:220 to make a hydrophobic solution;

(3)将疏水溶液与河沙按照质量比为1∶5~1∶8的比例混合,得到混合物;  (3) Mix the hydrophobic solution and the river sand according to the mass ratio of 1:5 to 1:8 to obtain a mixture;

(4)将混合物进行干燥,得到防渗层材料。  (4) Drying the mixture to obtain the anti-seepage layer material. the

复合填料层的填料采取以下方法制成:  The filler of the composite filler layer is made by the following methods:

首先,将粒径为2~8mm、质量比为10-20%的石灰石,粒径为3~10mm、质量比为20-30%的煤渣,粒径小于2mm、质量比为5-10%的粉煤灰,粒径小于2mm、质量比为15-20%的粘土,粒径为3~8mm、质量比为5-20%的火山岩,粒径为2~8mm、质量比为5-10%的改性硅藻土,以及质量比为5-10%的水进行混合并搅拌均匀;  First, limestone with a particle size of 2-8mm and a mass ratio of 10-20%, cinder with a particle size of 3-10mm and a mass ratio of 20-30%, and cinders with a particle size of less than 2mm and a mass ratio of 5-10% Fly ash, clay with a particle size of less than 2mm and a mass ratio of 15-20%, volcanic rock with a particle size of 3-8mm and a mass ratio of 5-20%, a particle size of 2-8mm and a mass ratio of 5-10% The modified diatomite, and water with a mass ratio of 5-10% are mixed and stirred evenly;

其次,将搅拌均匀的浆料导入模具中,并在80-120Pa/mm2的压力下压制成型,脱模后自然风干,最终制得复合填料层所需要的填料。  Secondly, the uniformly stirred slurry is introduced into the mold, and pressed under the pressure of 80-120Pa/mm2, and then air-dried naturally after demoulding, and finally the filler required for the composite filler layer is obtained. the

本发明的具体运行原理为:  Concrete operation principle of the present invention is:

(1)当污水被注入人工湿地池后,先通过种植层,种植层通过植物根系去除部分污染物;  (1) After the sewage is injected into the constructed wetland pool, it first passes through the planting layer, and the planting layer removes some pollutants through the plant root system;

(2)经过种植层初步净化的污水流至砾石层,砾石层通过过滤对大颗粒杂质进行阻挡迂回,并利用其表面微生物的物理、化学和生化反应联合作用去除被过滤的大颗粒杂质,对污水进行二次净化;  (2) The sewage that has been preliminarily purified by the planting layer flows to the gravel layer. The gravel layer blocks and detours the large-particle impurities through filtration, and uses the combined action of the physical, chemical and biochemical reactions of microorganisms on its surface to remove the filtered large-particle impurities. Secondary purification of sewage;

(3)经过砾石层净化的污水会进入复合填料层进行再次净化,而复合填料层的结构及制备成分上的创新,使其具备高净化能力,对污水进行彻底净化;  (3) The sewage purified by the gravel layer will enter the composite packing layer for further purification, and the innovation of the structure and preparation components of the composite packing layer enables it to have high purification capacity and thoroughly purify the sewage;

(4)经复合填料层彻底净化后的污水,最终由排水管排出。  (4) The sewage thoroughly purified by the composite packing layer is finally discharged by the drain pipe. the

在运行时,砾石层的供气管通过其上表面的供气孔,只向人工湿地池的上端供应氧气,促进了人工湿地池上端好痒区的硝化反应,以及人工湿地池下端厌氧区的反硝化反应,提高了人工湿地的净化能力。  During operation, the air supply pipe of the gravel layer only supplies oxygen to the upper end of the constructed wetland pool through the air supply holes on its upper surface, which promotes the nitrification reaction in the itchy area at the upper end of the constructed wetland pool and the reaction in the anaerobic area at the lower end of the constructed wetland pool. The nitrification reaction improves the purification ability of the constructed wetland. the

防渗层材料效果实验:  Material effect experiment of anti-seepage layer:

实施例1:  Example 1:

按照上述防渗层材料的制成方法,将防渗层组成材料按照以下质量份进行配比:  According to the preparation method of the above-mentioned anti-seepage layer materials, the composition materials of the anti-seepage layer are proportioned according to the following parts by mass:

水溶性二氧化硅,0.06份;  Water-soluble silicon dioxide, 0.06 parts;

甲基硅酸钾,0.08份;  Potassium methyl silicate, 0.08 parts;

硅酸钾,0.4份;  Potassium silicate, 0.4 parts;

河沙,260份;  River sand, 260 parts;

以及水,70份。  and water, 70 parts. the

将制成的防渗层材料进行如下实验。  The prepared anti-seepage layer material was subjected to the following experiments. the

实验1:  Experiment 1:

首先,准备一个玻璃容器,用玻璃容器的形状模拟人工湿地池,玻璃容器的形状为长方形,深度为150cm,容器底部留有漏水口;其次,将按照上述方法制备的防渗层材料铺在容器的底部,使防渗层材料完全覆盖口水口,防渗层材料铺设的厚度为2-4cm;然后,向玻璃容器中注入140cm的人工湿地池平时需要处理的废液;最后,在容器底部漏水口下端放置一张干燥的滤纸,观察玻璃容器在24小时内的渗水状况;  First, prepare a glass container, using the shape of the glass container to simulate the artificial wetland pool. The shape of the glass container is rectangular, the depth is 150cm, and there is a leak at the bottom of the container; secondly, spread the anti-seepage layer material prepared according to the above method on the container At the bottom of the bottom, make the anti-seepage layer material completely cover the spout, and the thickness of the anti-seepage layer material is 2-4cm; then, inject 140cm of waste liquid that usually needs to be treated in the constructed wetland pool into the glass container; finally, leak water at the bottom of the container Place a piece of dry filter paper at the lower end of the mouth, and observe the water seepage of the glass container within 24 hours;

结果:通过观察,在容器加水24小时内,容器底部的滤纸干燥,无废水渗出。此结果说明本发明的防渗层可以满足对高液位废液的防渗需求。  Result: By observation, within 24 hours of adding water to the container, the filter paper at the bottom of the container was dry and no waste water seeped out. This result shows that the anti-seepage layer of the present invention can meet the anti-seepage requirements for high-level waste liquid. the

实验2:  Experiment 2:

与实验1不同的是向玻璃容器中注入140cm、温度为40摄氏度的废液,并分别在第1周、第2周、第3周、第4周、第2个月、第3个月观察容器底部漏水口的渗水状况并进行统计。  The difference from Experiment 1 is that 140 cm of waste liquid at a temperature of 40 degrees Celsius was injected into the glass container, and the observations were made in the first week, the second week, the third week, the fourth week, the second month, and the third month. The seepage status of the water leakage at the bottom of the container and make statistics. the

结果:通过观察,在统计期间,容器底部的滤纸干燥,无废水渗出。此结果说明本发明的防渗层抗高温、耐老化效果好。  Results: By observation, during the statistical period, the filter paper at the bottom of the container was dry and no waste water seeped out. This result shows that the anti-seepage layer of the present invention has good effects of high temperature resistance and aging resistance. the

实施例2:  Example 2:

按照上述防渗层材料的制成方法,将防渗层组成材料按照以下质量份进行配比:  According to the preparation method of the above-mentioned anti-seepage layer materials, the composition materials of the anti-seepage layer are proportioned according to the following parts by mass:

水溶性二氧化硅,0.065份;  Water-soluble silicon dioxide, 0.065 parts;

甲基硅酸钾,0.09份;  Potassium methyl silicate, 0.09 parts;

硅酸钾,0.45份;  Potassium silicate, 0.45 parts;

河沙,1030份;  River sand, 1030 parts;

以及水,135份。  and water, 135 parts. the

将制成的防渗层材料进行如下实验。  The prepared anti-seepage layer material was subjected to the following experiments. the

实验1:  Experiment 1:

首先,准备一个玻璃容器,用玻璃容器的形状模拟人工湿地池,玻璃容器的形状为长方形,深度为150cm,容器底部留有漏水口;其次,将按照上述方法制备的防渗层材料铺在容器的底部,使防渗层材料完全覆盖口水口,防渗层材料铺设的厚度为2-4cm;然后,向玻璃容器中注入140cm的人工湿地池平时需要处理的废液;最后,在容器底部漏水口下端放置一张干燥的滤纸,观察玻璃容器在24小时内的渗水状况;  First, prepare a glass container, using the shape of the glass container to simulate the artificial wetland pool. The shape of the glass container is rectangular, the depth is 150cm, and there is a leak at the bottom of the container; secondly, spread the anti-seepage layer material prepared according to the above method on the container At the bottom of the bottom, make the anti-seepage layer material completely cover the spout, and the thickness of the anti-seepage layer material is 2-4cm; then, inject 140cm of waste liquid that usually needs to be treated in the constructed wetland pool into the glass container; finally, leak water at the bottom of the container Place a piece of dry filter paper at the lower end of the mouth, and observe the water seepage of the glass container within 24 hours;

结果:通过观察,在容器加水24小时内,容器底部的滤纸干燥,无废水渗出。此结果说明本发明的防渗层可以满足对高液位废液的防渗需求。  Result: By observation, within 24 hours of adding water to the container, the filter paper at the bottom of the container was dry and no waste water seeped out. This result shows that the anti-seepage layer of the present invention can meet the anti-seepage requirements for high-level waste liquid. the

实验2:  Experiment 2:

与实验1不同的是向玻璃容器中注入140cm、温度为40摄氏度的废液,并分别在第1周、第2周、第3周、第4周、第2个月、第3个月观察容器底部漏水口的渗水状况并进行统计。  The difference from Experiment 1 is that 140 cm of waste liquid at a temperature of 40 degrees Celsius was injected into the glass container, and the observations were made in the first week, the second week, the third week, the fourth week, the second month, and the third month. The seepage status of the water leakage at the bottom of the container and make statistics. the

结果:通过观察,在统计期间,容器底部的滤纸干燥,无废水渗出。此结果说明本发明的防渗层抗高温、耐老化效果好。  Results: By observation, during the statistical period, the filter paper at the bottom of the container was dry and no waste water seeped out. This result shows that the anti-seepage layer of the present invention has good effects of high temperature resistance and aging resistance. the

实施例3:  Example 3:

按照上述防渗层材料的制成方法,将防渗层组成材料按照以下质量份进行配比:  According to the preparation method of the above-mentioned anti-seepage layer materials, the composition materials of the anti-seepage layer are proportioned according to the following parts by mass:

水溶性二氧化硅,0.07份;  Water-soluble silicon dioxide, 0.07 parts;

甲基硅酸钾,0.1份;  Potassium methyl silicate, 0.1 part;

硅酸钾,0.5份;  Potassium silicate, 0.5 parts;

河沙,1800份;  River sand, 1800 parts;

以及水,200份。  and water, 200 parts. the

将制成的防渗层材料进行如下实验。  The prepared anti-seepage layer material was subjected to the following experiments. the

实验1:  Experiment 1:

首先,准备一个玻璃容器,用玻璃容器的形状模拟人工湿地池,玻璃容器的形状为长方形,深度为150cm,容器底部留有漏水口;其次,将按照上述方法制备的防渗层材料铺在容器的底部,使防渗层材料完全覆盖口水口,防渗层材料铺设的厚度为2-4cm;然后,向玻璃容器中注入140cm的人工湿地池平时需要处理的废液;最后,在容器底部漏水口下端放置一张干燥的滤纸,观察玻璃容器在24小时内的渗水状况;  First, prepare a glass container, using the shape of the glass container to simulate the artificial wetland pool. The shape of the glass container is rectangular, the depth is 150cm, and there is a leak at the bottom of the container; secondly, spread the anti-seepage layer material prepared according to the above method on the container At the bottom of the bottom, make the anti-seepage layer material completely cover the spout, and the thickness of the anti-seepage layer material is 2-4cm; then, inject 140cm of waste liquid that usually needs to be treated in the constructed wetland pool into the glass container; finally, leak water at the bottom of the container Place a piece of dry filter paper at the lower end of the mouth, and observe the water seepage of the glass container within 24 hours;

结果:通过观察,在容器加水24小时内,容器底部的滤纸干燥,无废水渗出。此结果说明本发明的防渗层可以满足对高液位废液的防渗需求。  Result: By observation, within 24 hours of adding water to the container, the filter paper at the bottom of the container was dry and no waste water seeped out. This result shows that the anti-seepage layer of the present invention can meet the anti-seepage requirements for high-level waste liquid. the

实验2:  Experiment 2:

与实验1不同的是向玻璃容器中注入140cm、温度为40摄氏度的废液,并分别在第1周、第2周、第3周、第4周、第2个月、第3个月观察容器底部漏水口的渗水状况并进行统计。  The difference from Experiment 1 is that 140 cm of waste liquid at a temperature of 40 degrees Celsius was injected into the glass container, and the observations were made in the first week, the second week, the third week, the fourth week, the second month, and the third month. The seepage status of the water leakage at the bottom of the container and make statistics. the

结果:通过观察,在统计期间,容器底部的滤纸干燥,无废水渗出。此结果说明本发明的防渗层抗高温、耐老化效果好。  Results: By observation, during the statistical period, the filter paper at the bottom of the container was dry and no waste water seeped out. This result shows that the anti-seepage layer of the present invention has good effects of high temperature resistance and aging resistance. the

以上所述实施例仅表达了本发明的实施方式,其描述较为具体和详细,但并不能因此而理解为对本发明型专利范围的限制。应当指出的是,对于本领域的普通技术人员来说,在不脱离本发明的前提下,还可以做出若干变形和改进,这些都属于本发明的保护范围。因此,本发明专利的保护范围应以所附权利要求为准。  The above-mentioned embodiments only express the implementation manner of the present invention, and the description thereof is relatively specific and detailed, but should not be construed as limiting the patent scope of the present invention. It should be noted that, for those skilled in the art, several modifications and improvements can be made without departing from the present invention, and these all belong to the protection scope of the present invention. Therefore, the protection scope of the patent for the present invention should be based on the appended claims. the

Claims (7)

1. antiseepage artificial wet land system, comprise bottom and the artificial swamp pond that is provided with impervious barrier all around, it is characterized in that: described artificial swamp pond from top to bottom set gradually plant wetland plant and be used for to sewage carry out primary purification the plantation layer, be used for to sewage carry out secondary-cleaned gravel bed, be used for compounded mix layer and water shoot that sewage is purified again, described impervious barrier is made by following materials in parts by mass:
Water-soluble silicon-dioxide, 0.06~0.07 part;
Methyl siliconic acid potassium, 0.08~0.1 part;
Potassium silicate, 0.4~0.5 part;
River sand, 260 parts~1800 parts;
And water, 70~220 parts.
2. antiseepage artificial wet land system according to claim 1, it is characterized in that: described artificial swamp pond is rectangle, and the long-width ratio in described rectangle artificial swamp pond is 5:1~10:1, and the degree of depth is 100cm~140cm.
3. antiseepage artificial wet land system according to claim 1 is characterized in that: be coated with mud on the described plantation layer, the thickness of described mud is 20cm~30cm.
4. antiseepage artificial wet land system according to claim 1, it is characterized in that: described compounded mix layer is made by the material of following mass ratio:
Particle diameter is the Wingdale of 2~8mm, 10%-20%;
Particle diameter is the cinder of 3~10mm, 20%-30%;
Particle diameter is less than the flyash of 2mm, 5%-10%;
Particle diameter is less than the clay of 2mm, 15%-20%;
Particle diameter is 3~8mm volcanics, 5%-20%;
Particle diameter is 2~8mm modification infusorial earth, 5%-10%;
And water, 5%-10%.
5. antiseepage artificial wet land system according to claim 4, it is characterized in that: the porosity of described compounded mix layer 〉=30%, volume density are 1200~1500Kg/m 3, permeation rate is 15~20m/h.
6. antiseepage artificial wet land system according to claim 1; it is characterized in that: described antiseepage artificial wet land system also comprises an air feeder; the air-supply duct of air feeder is horizontal to be inserted in the middle and upper part in described artificial swamp pond and is positioned at gravel bed; the upper surface of described air-supply duct evenly is provided with a plurality of air vents; air vent is coated with the screening glass of coupling; described screening glass and air-supply duct are started screening glass for flexibly connecting when air feed, reset when air feed not.
7. antiseepage artificial wet land system according to claim 6; it is characterized in that: described air feeder also comprises the air compressor that is connected with air-supply duct; described air-supply duct is with the ventilative webmaster of hard of protectiveness outward, and the grid diameter of described ventilative webmaster is less than the particle diameter of gravel bed filler of living in.
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Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111533369A (en) * 2020-04-24 2020-08-14 北京土人城市规划设计股份有限公司 Wetland sewage purification system

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5733453A (en) * 1996-07-15 1998-03-31 Azurea, Inc. Wastewater treatment system and method
CN201809224U (en) * 2010-10-11 2011-04-27 山东大学 Grading-type vertical current constructed wetland system
CN102503344A (en) * 2011-10-20 2012-06-20 北京市农林科学院 Antiseepage material and preparation method thereof
CN202430056U (en) * 2011-09-01 2012-09-12 华南理工大学 Green belt gutter constructed wetland device for treatment of road rainfall runoff pollution
CN102923857A (en) * 2012-11-09 2013-02-13 山东大学 Anoxic-aerobic vertical flow artificial wetland system
CN102942253A (en) * 2012-10-31 2013-02-27 江苏大学 Constructed wetland sewage treatment method and system

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5733453A (en) * 1996-07-15 1998-03-31 Azurea, Inc. Wastewater treatment system and method
CN201809224U (en) * 2010-10-11 2011-04-27 山东大学 Grading-type vertical current constructed wetland system
CN202430056U (en) * 2011-09-01 2012-09-12 华南理工大学 Green belt gutter constructed wetland device for treatment of road rainfall runoff pollution
CN102503344A (en) * 2011-10-20 2012-06-20 北京市农林科学院 Antiseepage material and preparation method thereof
CN102942253A (en) * 2012-10-31 2013-02-27 江苏大学 Constructed wetland sewage treatment method and system
CN102923857A (en) * 2012-11-09 2013-02-13 山东大学 Anoxic-aerobic vertical flow artificial wetland system

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111533369A (en) * 2020-04-24 2020-08-14 北京土人城市规划设计股份有限公司 Wetland sewage purification system

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