CN104003527B - A kind of polluted water body in-situ prosthetic device and method thereof - Google Patents

A kind of polluted water body in-situ prosthetic device and method thereof Download PDF

Info

Publication number
CN104003527B
CN104003527B CN201410248342.5A CN201410248342A CN104003527B CN 104003527 B CN104003527 B CN 104003527B CN 201410248342 A CN201410248342 A CN 201410248342A CN 104003527 B CN104003527 B CN 104003527B
Authority
CN
China
Prior art keywords
water
microbial reaction
water inlet
reaction case
plant
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
Application number
CN201410248342.5A
Other languages
Chinese (zh)
Other versions
CN104003527A (en
Inventor
申战辉
沈帅兵
王春峰
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Henan Normal University
Original Assignee
Henan Normal University
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Henan Normal University filed Critical Henan Normal University
Priority to CN201410248342.5A priority Critical patent/CN104003527B/en
Publication of CN104003527A publication Critical patent/CN104003527A/en
Application granted granted Critical
Publication of CN104003527B publication Critical patent/CN104003527B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • 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
    • 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
    • Y02W10/30Wastewater or sewage treatment systems using renewable energies
    • Y02W10/33Wastewater or sewage treatment systems using renewable energies using wind energy
    • 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
    • Y02W10/30Wastewater or sewage treatment systems using renewable energies
    • Y02W10/37Wastewater or sewage treatment systems using renewable energies using solar energy

Landscapes

  • Biological Treatment Of Waste Water (AREA)

Abstract

本发明公开了一种污染水体原位修复装置及其方法。本发明的技术方案要点为:一种污染水体原位修复装置,包括微生物处理系统和设置于微生物处理系统上方的植物修复系统,其中微生物处理系统主要由微生物反应箱、漂浮箱、排水泵、悬浮填料、风管、风机、曝气头和自动进水阀组成,所述的植物修复系统包括植物固定层和固定于植物固定层上的功能植物。本发明还公开了使用该污染水体原位修复装置净化水体的方法。本发明利用微生物自身降解水中的污染物以及植物吸收水中的氮磷等元素进而实现原位修复污染水体的目的。

The invention discloses an in-situ restoration device for polluted water bodies and a method thereof. The main points of the technical solution of the present invention are: an in-situ remediation device for polluted water, including a microbial treatment system and a phytoremediation system arranged above the microbial treatment system, wherein the microbial treatment system mainly consists of a microbial reaction tank, a floating tank, a drainage pump, a suspension The phytoremediation system includes a plant fixed layer and functional plants fixed on the plant fixed layer. The invention also discloses a water purification method using the in-situ restoration device for polluted water. The invention utilizes microorganisms to degrade pollutants in water and plants to absorb elements such as nitrogen and phosphorus in water to realize the purpose of in-situ restoration of polluted water bodies.

Description

一种污染水体原位修复装置及其方法Device and method for in-situ remediation of polluted water

技术领域 technical field

本发明属于环境保护中的水污染处理技术领域,具体涉及一种污染水体原位修复装置及其方法。 The invention belongs to the technical field of water pollution treatment in environmental protection, and in particular relates to an in-situ restoration device for polluted water and a method thereof.

背景技术 Background technique

随着社会的进步和科技的发展,各种工业工厂的数量与日俱增。这些工厂在推动经济发展的同时也给生物生活的环境带来了威胁,环境问题已经从局部发展为全球性的威胁。水是生命之源,而大量的污染物进入水体,致使水体富营养化,水环境指标严重下降,对生物的生存构成了极其严重的威胁,比如我国的淮河流域。世界各国都越来越重视污水的处理和回用技术,实现水资源的可持续利用,遏制水污染的加剧趋势,迫在眉睫。 With the progress of society and the development of science and technology, the number of various industrial factories is increasing day by day. While promoting economic development, these factories have also brought threats to the living environment. Environmental problems have developed from local to global threats. Water is the source of life, and a large number of pollutants enter the water body, resulting in eutrophication of the water body, a serious drop in water environment indicators, and an extremely serious threat to the survival of organisms, such as the Huaihe River Basin in my country. All countries in the world are paying more and more attention to sewage treatment and reuse technology, realizing the sustainable use of water resources and curbing the aggravation of water pollution are imminent.

目前改善水体水质的方法主要有:物理方法、化学方法和生物方法三种。物理方法是用格栅、筛网、沉沙池、沉淀池和隔油池等构筑物去除废水中的固体悬浮物和浮油,初步减轻废水的腐化程度,这种方法往往达不到彻底根除的效果。化学方法是加入某些化学物质,通过化学反应中和、氧化、还原、分解、絮凝和化学沉淀等改变废水中污染物的化学性质,使之发生化学或物理状态的变化,进而从水中除去,这种方法有可能会引入新的污染物,不利于被推广使用。生物方法是利用微生物的代谢作用,使废水中的有机污染物氧化降解成无害物质的方法,这种方法又叫生物化学处理法,是处理有机废水最重要的方法。其中废水的生物处理法是基于微生物通过酶的作用将复杂的有机物转化为简单的物质,把有毒的物质转化为无毒的物质的方法。三种方法相比较,生物方法具有明显的优势,生物方法投资小,效果明显,而且不产生二次污染,因此生物方法在水环境治理方面得到了广泛的应用。 At present, there are three main methods to improve water quality: physical methods, chemical methods and biological methods. The physical method is to use structures such as grids, screens, grit chambers, sedimentation tanks and grease traps to remove suspended solids and slick oil in wastewater, and initially reduce the degree of corrosion of wastewater. This method often fails to completely eradicate Effect. The chemical method is to add certain chemical substances, change the chemical properties of the pollutants in the wastewater through chemical reactions such as neutralization, oxidation, reduction, decomposition, flocculation and chemical precipitation, so as to change their chemical or physical state, and then remove them from the water. This method may introduce new pollutants, which is not conducive to its promotion and use. The biological method is to use the metabolism of microorganisms to oxidize and degrade the organic pollutants in the wastewater into harmless substances. This method is also called biochemical treatment and is the most important method for treating organic wastewater. Among them, the biological treatment method of wastewater is based on the method that microorganisms convert complex organic matter into simple substances and toxic substances into non-toxic substances through the action of enzymes. Compared with the three methods, the biological method has obvious advantages, the investment of the biological method is small, the effect is obvious, and it does not produce secondary pollution, so the biological method has been widely used in water environment treatment.

在生物方法中又包括异位修复和原位修复。其中异位修复是将受污染的水体抽出再进行处理的技术,该技术在短期内处理量大,处理效果较高,但长期应用普遍存在着拖尾、反弹等现象,最终降低了处理效率,增加了处理成本。原位修复技术以其修复彻底、处理污染物种类多、时间相对较短和成本相对低廉等优势在水污染修复领域得到了广泛的应用。 Biological methods also include ectopic repair and in situ repair. Among them, ex-situ remediation is a technology that pumps out the polluted water body and then treats it. This technology has a large amount of treatment in a short period of time and a high treatment effect. However, long-term application generally has phenomena such as tailing and rebound, which ultimately reduces the treatment efficiency. Increased processing costs. In-situ remediation technology has been widely used in the field of water pollution remediation due to its advantages of thorough remediation, various types of pollutants, relatively short time and relatively low cost.

中国专利申请号200610076417.1,授权公告日为2008年3月5日,发明创造名称为水体原位修复生态反应器,该发明利用风能、水能、太阳能和生物植物质能,在动态中对受损水体进行原位修复,不仅能够提高水体修复净化效率,无二次污染,而且还可降低成本,但受自然天气因素的制约,影响水体原位修复生态反应器的净化效果。中国专利申请号200310103050.4,公开日为2004年10月27日,发明创造名称为水平旋流悬浮载体生物膜反应器及其水体原位修复方法,该发明从水体原位修复反应器的特点出发,对反应器的结构、载体选择及其投加量等进行了优化,从而使得反应器在正常运行时,载体颗粒能在较高载体投加量、较低曝气量的情况下充分悬浮,并维持水平旋流的状态,从而有效提高反应器对有机污染物和氨氮的去除率,但此装置受水流的影响较大,难以在河流湖泊中控制其位置并且人工操作较多,管理复杂。此外,其它专利的技术方案也都存在不同程度的缺点和不足。 Chinese patent application number 200610076417.1, authorized announcement date is March 5, 2008, the name of the invention is ecological reactor for in-situ restoration of water body. In-situ restoration of water body can not only improve the efficiency of water body restoration and purification without secondary pollution, but also reduce the cost. However, due to the constraints of natural weather factors, the purification effect of the in-situ restoration of water body ecological reactor will be affected. Chinese Patent Application No. 200310103050.4, published on October 27, 2004, the invention is called a horizontal swirl suspension carrier biofilm reactor and its in-situ repair method for water body. The invention starts from the characteristics of the in-situ repair reactor for water body. The structure of the reactor, carrier selection and dosage are optimized, so that when the reactor is in normal operation, the carrier particles can be fully suspended under the condition of higher carrier dosage and lower aeration, and Maintain the state of horizontal swirling flow, thereby effectively improving the removal rate of organic pollutants and ammonia nitrogen in the reactor, but this device is greatly affected by water flow, it is difficult to control its position in rivers and lakes, and there are many manual operations and complicated management. In addition, the technical solutions of other patents also have various shortcomings and deficiencies.

发明内容 Contents of the invention

本发明的目的是针对我国污染水体的现状,结合微生物处理技术和水体植物修复于一体,提供了一种污染水体原位修复装置及其方法。 The purpose of the present invention is to provide an in-situ repairing device and method for polluted water in combination with microbial treatment technology and water phytoremediation, aiming at the current situation of polluted water in my country.

本发明的技术方案为:一种污染水体原位修复装置,其特征在于包括微生物处理系统和设置于微生物处理系统上方的植物修复系统,其中微生物处理系统主要由微生物反应箱、漂浮箱、排水泵、悬浮填料、风管、风机、曝气头和自动进水阀组成,所述的漂浮箱通过三角架固定于微生物反应箱外侧顶部的周围,排水泵固定于漂浮箱之上,排水泵的进水口与伸入到微生物反应箱中的排水管相连接,排水泵的出水口与外界相通,悬浮填料悬浮于微生物反应箱内的水中,风管铺设于整个微生物反应箱的底部,风管的外端与设置于漂浮箱上的风机出风口相连接,所述的风机与排水泵分别与外部的电缆相连接,曝气头固定于微生物反应箱底部的风管上,自动进水阀设置于微生物反应箱的底部,该自动进水阀包括阀体和设置于阀体上的进水管与出水管,其中进水管与外界相通,出水管与微生物反应箱相连通;所述的植物修复系统包括植物固定层和固定于植物固定层上的功能植物,其中植物固定层通过三角架固定于微生物反应箱上部的四分之一处,植物固定层主要由穿孔塑料板和分布于穿孔塑料板上方的鹅卵石、砂石、泥炭或岩棉组成,所述的功能植物固定于植物固定层上,该功能植物为芦苇、美人蕉、水葫芦或灯芯草中的一种或多种。 The technical solution of the present invention is: an in-situ restoration device for polluted water, which is characterized in that it includes a microbial treatment system and a phytoremediation system arranged above the microbial treatment system, wherein the microbial treatment system is mainly composed of a microbial reaction tank, a floating tank, and a drainage pump. , suspended filler, air duct, blower fan, aeration head and automatic water inlet valve, the floating tank is fixed around the top of the microbial reaction tank through a tripod, the drainage pump is fixed on the floating tank, and the inlet of the drainage pump The water outlet is connected to the drainage pipe extending into the microbial reaction box, the outlet of the drainage pump is connected to the outside world, the suspended filler is suspended in the water in the microbial reaction box, and the air duct is laid at the bottom of the entire microbial reaction box. The end is connected to the air outlet of the fan installed on the floating tank, the fan and the drainage pump are respectively connected to the external cables, the aeration head is fixed on the air pipe at the bottom of the microbial reaction tank, and the automatic water inlet valve is set on the microbial reactor. The bottom of the reaction tank, the automatic water inlet valve includes a valve body and an inlet pipe and an outlet pipe arranged on the valve body, wherein the inlet pipe communicates with the outside world, and the outlet pipe communicates with the microbial reaction tank; the phytoremediation system includes a plant The fixed layer and the functional plants fixed on the plant fixed layer, wherein the plant fixed layer is fixed on the upper quarter of the microbial reaction box through a tripod, and the plant fixed layer is mainly composed of perforated plastic plates and pebbles distributed above the perforated plastic plates , sand, peat or rock wool, and the functional plants are fixed on the plant fixing layer, and the functional plants are one or more of reeds, cannas, water hyacinths or rushes.

本发明所述的污染水体原位修复方法,其特征在于具体步骤如下:首先将污染水体原位修复装置固定于污染水体中,通过自动进水阀控制微生物反应箱内的水位,当微生物反应箱内的水位低于设定位置时自动进水阀自动开启开始进水,当微生物反应箱内的水位高于设定位置时自动进水阀自动关闭停止进水,当微生物反应箱内的水位达到设定高度时进入曝气阶段,风机自动开启进行曝气,曝气3-8h后进入沉淀阶段,沉淀0.5-2h后排水泵自动开启开始排水,排水泵由设定液位自动控制停止,当液位达到设定位置时排水泵停止运行,然后自动进水阀自动开启开始进水,进入下一个循环。 The in-situ remediation method of polluted water body according to the present invention is characterized in that the specific steps are as follows: first, the in-situ remediation device for polluted water body is fixed in the polluted water body, and the water level in the microbial reaction tank is controlled by an automatic water inlet valve. When the water level in the microbial reaction tank is lower than the set position, the automatic water inlet valve will automatically open and start water intake. When the water level in the microbial reaction tank is higher than the set position, the automatic water intake valve will automatically close and stop water intake. When the height is set, it enters the aeration stage, the fan is automatically turned on for aeration, and after 3-8 hours of aeration, it enters the sedimentation stage. After 0.5-2 hours of sedimentation, the drainage pump automatically starts to drain water, and the drainage pump is automatically controlled by the set liquid level to stop. When the liquid level reaches the set position, the drainage pump stops running, and then the automatic water inlet valve automatically opens to start water intake, and enters the next cycle.

本发明的与现有技术相比具有以下有益效果:(1)利用微生物自身降解水中的污染物以及植物吸收水中的氮磷等元素进而实现原位修复污染水体的目的;(2)材料易得,成本低廉,符合水污染处理中经济性的要求;(3)处理效果显著,无二次污染,本技术利用微生物和植物的共同作用进行污染水体的处理,经济环保,符合可持续发展;(4)稳定性好,漂浮箱能够让整个装置在水面上维持稳定,保证每个环节的顺利进行;(5)整个修复运行过程自动化程度高,节省运行管理人力物力;(6)生态景观效果好,功能植物可形成水上景观,美化水上环境。 Compared with the prior art, the present invention has the following beneficial effects: (1) Utilize microorganisms to degrade pollutants in water and plants absorb nitrogen, phosphorus and other elements in water to achieve the purpose of in situ repairing polluted water bodies; (2) materials are easy to obtain , low cost, in line with the economic requirements of water pollution treatment; (3) The treatment effect is remarkable, no secondary pollution, this technology uses the joint action of microorganisms and plants to treat polluted water, economical and environmentally friendly, in line with sustainable development; ( 4) Good stability, the floating box can keep the whole device stable on the water surface, ensuring the smooth progress of each link; (5) The whole repair operation process is highly automated, saving manpower and material resources for operation management; (6) The ecological landscape effect is good , Functional plants can form a water landscape and beautify the water environment.

附图说明 Description of drawings

图1是本发明的结构示意图。 Fig. 1 is a structural schematic diagram of the present invention.

图面说明:1、微生物反应箱,2、漂浮箱,3、排水泵,4、悬浮填料,5、风管,6、风机,7、曝气头,8、机械自动进水泵,9、植物固定层,10、功能植物。 Drawing description: 1. Microbial reaction box, 2. Floating box, 3. Drainage pump, 4. Suspended filler, 5. Air duct, 6. Fan, 7. Aeration head, 8. Mechanical automatic water inlet pump, 9. Plant Fixed layer, 10, functional plants.

具体实施方式 detailed description

结合附图详细描述实施例。一种污染水体原位修复装置,包括微生物处理系统和设置于微生物处理系统上方的植物修复系统,其中微生物处理系统主要由微生物反应箱1、漂浮箱2、排水泵3、悬浮填料4、风管5、风机6、曝气头7和自动进水阀8组成,所述的漂浮箱2通过三角架固定于微生物反应箱1外侧顶部的周围,漂浮箱2使得整个装置在重力和浮力的作用下达到平衡,以维持在水中的稳定性,漂浮箱2采用尺寸为0.5m*0.5m*5m的熟料漂浮箱,微生物反应箱1采用尺寸为5m*5m*2m铸铁箱,排水泵3固定于漂浮箱2之上,排水泵3的进水口与伸入到微生物反应箱1中的排水管相连接,排水泵3的出水口与外界相通,排水泵3用于排出处理后的水体使微生物反应箱1内的水位下降至箱体高度的二分之一处,悬浮填料4悬浮于微生物反应箱1内的水中,悬浮填料4采用有机共聚物材质和空心圆立体结构,在微生物反应箱1中可以自由浮动,悬浮填料4使得微生物的附着表面积增大,能在污水处理中取得很好的效果,风管5铺设于整个微生物反应箱1的底部,风管5可采用镀锌钢管或熟料管,风管5的外端与设置于漂浮箱2上的风机6出风口相连接,所述的风机6与排水泵3分别与外部的电缆相连接,风机6用于为微生物反应箱1运行过程中的曝气阶段提供压力空气,通过风管5输送到曝气头7,产生微小的气泡,提高微生物反应箱1中水的溶解氧,进而提高生化反应效率,曝气头7固定于微生物反应箱1底部的风管5上,自动进水阀8设置于微生物反应箱1的底部,该自动进水阀8包括阀体和设置于阀体上的进水管与出水管,其中进水管与外界相通,出水管与微生物反应箱1相连通,该自动进水阀8用于控制进水的开启和关闭,当微生物反应箱1中的水位低于设定位置时自动开启开始进水,当微生物反应箱1中的水位高于设定位置时自动关闭停止进水,微生物反应箱1的运行分为进水-曝气-沉淀-排水4个阶段,进水阶段由自动进水阀8自动控制,进水时间为10-30min,曝气阶段由液位自动控制,当微生物反应箱1中液位达到设定位置时,风机6自动开启,曝气时间可根据水质设定,设定范围为3-8h,曝气结束后进入沉淀阶段,时间为0.5-2h,沉淀阶段结束后排水泵3自动开启开始排水,排水泵3由液位自动控制停止,当液位达到设定位置时排水泵3停止运行,然后自动进水阀8自动开启开始进水进入下一个循环;所述的植物修复系统包括植物固定层9和固定于植物固定层9上的功能植物10,其中植物固定层9通过三角架固定于微生物反应箱1上部的四分之一处,植物固定层9主要由穿孔塑料板和分布于穿孔塑料板上方的鹅卵石、砂石、泥炭或岩棉组成,所述的功能植物10固定于植物固定层9上,该功能植物10为芦苇、美人蕉、水葫芦或灯芯草中的一种或多种,功能植物10不仅能有效去除污染水体中氮磷等营养元素,净化水体水质,而且能够形成水上景观,美化水上环境。 Embodiments are described in detail with reference to the accompanying drawings. An in-situ remediation device for polluted water, including a microbial treatment system and a phytoremediation system arranged above the microbial treatment system, wherein the microbial treatment system mainly consists of a microbial reaction tank 1, a floating tank 2, a drainage pump 3, a suspended filler 4, and an air duct 5. Composed of fan 6, aeration head 7 and automatic water inlet valve 8, the floating box 2 is fixed around the top of the microbial reaction box 1 through a tripod, and the floating box 2 makes the whole device under the action of gravity and buoyancy To achieve balance, in order to maintain the stability in the water, the floating box 2 adopts a clinker floating box with a size of 0.5m*0.5m*5m, the microbial reaction box 1 adopts a cast iron box with a size of 5m*5m*2m, and the drainage pump 3 is fixed on Above the floating tank 2, the water inlet of the drainage pump 3 is connected to the drainage pipe extending into the microbial reaction tank 1, and the water outlet of the drainage pump 3 communicates with the outside world, and the drainage pump 3 is used to discharge the treated water to make the microorganisms react The water level in the box 1 drops to half of the height of the box body, and the suspended filler 4 is suspended in the water in the microbial reaction box 1. The suspended filler 4 is made of an organic copolymer material and a hollow circular three-dimensional structure. It can float freely, and the suspended filler 4 increases the surface area of microorganisms, which can achieve good results in sewage treatment. The air duct 5 is laid at the bottom of the entire microbial reaction box 1, and the air duct 5 can be galvanized steel pipe or clinker The outer end of the air pipe 5 is connected to the air outlet of the fan 6 arranged on the floating tank 2, and the fan 6 and the drainage pump 3 are connected to the external cables respectively, and the fan 6 is used to run the microbial reaction tank 1 The aeration stage in the process provides pressure air, which is transported to the aeration head 7 through the air duct 5 to generate tiny air bubbles to increase the dissolved oxygen in the water in the microbial reaction tank 1, thereby improving the efficiency of the biochemical reaction. The aeration head 7 is fixed on the microorganism On the air duct 5 at the bottom of the reaction box 1, an automatic water inlet valve 8 is arranged on the bottom of the microbial reaction box 1, and the automatic water inlet valve 8 includes a valve body and an inlet pipe and an outlet pipe arranged on the valve body, wherein the water inlet pipe and the outlet pipe The outside is connected, and the outlet pipe is connected with the microbial reaction box 1. The automatic water inlet valve 8 is used to control the opening and closing of the water inlet. When the water level in the microbial reaction box 1 is lower than the set position, it will automatically open and start water intake. When the water level in the microbial reaction box 1 is higher than the set position, it is automatically closed to stop the water intake. The operation of the microbial reaction box 1 is divided into four stages: water intake-aeration-sedimentation-drainage, and the water intake stage is automatically controlled by the automatic water inlet valve 8. Control, the water intake time is 10-30min, the aeration stage is automatically controlled by the liquid level, when the liquid level in the microbial reaction tank 1 reaches the set position, the fan 6 is automatically turned on, the aeration time can be set according to the water quality, the setting range 3-8h, enter the sedimentation stage after the aeration is over, the time is 0.5-2h, after the sedimentation stage is over, the drainage pump 3 will automatically start to start drainage, the drainage pump 3 will be automatically controlled by the liquid level to stop, and the water will be drained when the liquid level reaches the set position The pump 3 stops running, and then the automatic water inlet valve 8 automatically opens and starts to enter the next cycle; the phytoremediation system includes a plant fixation layer 9 and a functional plant 10 fixed on the plant fixation layer 9, wherein the plant fixation The layer 9 is fixed on the upper quarter of the microbial reaction box 1 through a tripod, and the plant fixing layer 9 is mainly composed of perforated plastic plates and pebbles, sandstone, peat or rock wool distributed above the perforated plastic plates. The functional plant 10 is fixed on the plant fixing layer 9, and the functional plant 10 is one or more of reed, canna, water hyacinth or rush. The functional plant 10 can not only effectively remove nutrients such as nitrogen and phosphorus in the polluted water body, but also purify Water quality, and can form water landscape, beautify the water environment.

本发明所述的污染水体原位修复方法,具体步骤如下:首先将污染水体原位修复装置固定于污染水体中,通过自动进水阀控制微生物反应箱内的水位最高为箱体高度的三分之二处,最低为箱体高度的二分之一处,当微生物反应箱内的水位低于二分之一箱体高度时自动进水阀开启开始进水,当微生物反应箱内水位高于三分之二箱体高度时自动进水阀关闭停止进水,当微生物反应箱内的水位达到三分之二箱体高度时进入曝气阶段,风机自动开启进行曝气,曝气4h后进入沉淀阶段,沉淀0.5h后排水泵自动开启开始排水,排水泵由液位自动控制停止,当液位达到二分之一箱体高度时排水泵停止运行,然后自动进水阀自动开启开始进水,进入下一个循环。 The in-situ restoration method of polluted water body according to the present invention, the specific steps are as follows: first, the in-situ restoration device for polluted water body is fixed in the polluted water body, and the water level in the microbial reaction box is controlled by an automatic water inlet valve to be up to one-third of the height of the box body The second place, the lowest is half of the height of the box. When the water level in the microbial reaction box is lower than one-half of the box height, the automatic water inlet valve opens to start water intake. When the water level in the microbial reaction box is higher than When the height of two-thirds of the box is high, the automatic water inlet valve is closed to stop water inflow. When the water level in the microbial reaction box reaches two-thirds of the box height, it enters the aeration stage, and the fan automatically turns on for aeration, and enters after 4 hours of aeration. In the sedimentation stage, after 0.5 hours of sedimentation, the drainage pump starts to drain automatically, and the drainage pump is automatically controlled by the liquid level to stop. When the liquid level reaches 1/2 of the height of the tank, the drainage pump stops running, and then the automatic water inlet valve automatically opens to start water intake , enter the next cycle.

以上实施例描述了本发明的基本原理、主要特征及优点,本行业的技术人员应该了解,本发明不受上述实施例的限制,上述实施例和说明书中描述的只是说明本发明的原理,在不脱离本发明原理的范围下,本发明还会有各种变化和改进,这些变化和改进均落入本发明保护的范围内。 The above embodiments have described the basic principles, main features and advantages of the present invention. Those skilled in the art should understand that the present invention is not limited by the above embodiments. What are described in the above embodiments and description are only to illustrate the principles of the present invention. Without departing from the scope of the principle of the present invention, there will be various changes and improvements in the present invention, and these changes and improvements all fall within the protection scope of the present invention.

Claims (1)

1. a polluted water body in-situ restorative procedure, it is characterized in that concrete steps are as follows: be first fixed in polluted-water by polluted water body in-situ prosthetic device, the water level in microbial reaction case is controlled by automatic water inlet valve, when the water level in microbial reaction case lower than automatic water inlet valve during desired location automatically open start water inlet, when the water level in microbial reaction case closes stopping water inlet automatically higher than automatic water inlet valve during desired location, aeration phase is entered when the water level in microbial reaction case reaches setting height, blower fan is automatically opened and is carried out aeration, precipitate phase is entered after aeration 3-8h, after precipitation 0.5-2h, beginning draining opened automatically by wet-pit, wet-pit stops by setting liquid automatic control, when liquid level reaches desired location, wet-pit is out of service, then automatic water inlet valve is automatically opened and is started water inlet, enter next circulation, described polluted water body in-situ prosthetic device comprises microbe treatment system and is arranged at the phytoremediation system above microbe treatment system, wherein microbe treatment system is primarily of microbial reaction case, flotation tank, wet-pit, floating stuffing, airduct, blower fan, aeration head and automatic water inlet valve composition, described flotation tank is fixed on around microbial reaction case outside top by tripod, wet-pit is fixed on flotation tank, the water-in of wet-pit is connected with the water shoot extend in microbial reaction case, the water outlet of wet-pit communicates with the external world, floating stuffing is suspended in the water in microbial reaction case, airduct is layed in the bottom of whole microbial reaction case, the outer end of airduct is connected with the fan outlet be arranged on flotation tank, described blower fan and wet-pit are connected with the cable of outside respectively, aeration head is fixed on the airduct bottom microbial reaction case, automatic water inlet valve is arranged at the bottom of microbial reaction case, this automatic water inlet valve comprises valve body and the water inlet pipe be arranged on valve body and rising pipe, wherein water inlet pipe communicates with the external world, rising pipe is connected with microbial reaction case, described phytoremediation system comprises plant immovable bed and is fixed on the function plant on plant immovable bed, wherein plant immovable bed is fixed on 1/4th places of microbial reaction upper box part by tripod, plant immovable bed is primarily of perforated plastic plate and the pebbles be distributed in above perforated plastic plate, sandstone, peat or rock wool composition, described function plant is fixed on plant immovable bed, and this function plant is one or more in reed, Canna generalis Bailey, Herba Eichhorniae or Medulla Junci.
CN201410248342.5A 2014-06-06 2014-06-06 A kind of polluted water body in-situ prosthetic device and method thereof Expired - Fee Related CN104003527B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201410248342.5A CN104003527B (en) 2014-06-06 2014-06-06 A kind of polluted water body in-situ prosthetic device and method thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201410248342.5A CN104003527B (en) 2014-06-06 2014-06-06 A kind of polluted water body in-situ prosthetic device and method thereof

Publications (2)

Publication Number Publication Date
CN104003527A CN104003527A (en) 2014-08-27
CN104003527B true CN104003527B (en) 2016-01-20

Family

ID=51364472

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201410248342.5A Expired - Fee Related CN104003527B (en) 2014-06-06 2014-06-06 A kind of polluted water body in-situ prosthetic device and method thereof

Country Status (1)

Country Link
CN (1) CN104003527B (en)

Families Citing this family (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104891641A (en) * 2015-06-15 2015-09-09 武汉中科水生环境工程股份有限公司 Vegetation bed aeration tank sewage treatment device
CN105347617A (en) * 2015-11-13 2016-02-24 河南师范大学 Microbial/plant compound purification method for in-situ remediation of polluted water body
CN105445432B (en) * 2015-12-24 2017-12-22 安徽锋亚环境技术有限公司 A kind of water sludge interface materialization regulator control system for landscape water body in-situ immobilization
CN105906047B (en) * 2016-05-05 2019-06-11 江苏奥尼斯环保科技有限公司 Integrated water body in-situ remediation equipment and application thereof
CN106830369A (en) * 2017-03-23 2017-06-13 西安建筑科技大学 A kind of biological prosthetic self-reversal system and device of active solar energy
CN109006283B (en) * 2018-08-15 2021-02-19 绩溪袁稻农业产业科技有限公司 Method for planting Dactylicapnos asiaticus
CN109052649B (en) * 2018-10-31 2023-08-29 青岛思普润水处理股份有限公司 Micro-power mixed sewage treatment device
CN111777182A (en) * 2020-07-31 2020-10-16 江苏环保产业技术研究院股份公司 An oxygen-enriched bioreactor suitable for in-situ remediation of micro-polluted water bodies
CN117330720A (en) * 2023-09-22 2024-01-02 西安西热水务环保有限公司 A test device for water body restoration chemicals combined with aquatic plants to collaboratively repair polluted water bodies

Family Cites Families (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP3439576B2 (en) * 1995-08-10 2003-08-25 株式会社荏原製作所 River purification method and purification device
CN1137862C (en) * 2000-11-09 2004-02-11 中国科学院石家庄农业现代化研究所 Domestic sewage treating system
CN1246231C (en) * 2003-10-31 2006-03-22 清华大学 Reactor of biomembrane of suspended carrier on horizon eddy flow and repairing method on site of water body
CN2703400Y (en) * 2004-04-21 2005-06-08 中国水产科学研究院渔业机械仪器研究所 Floating island biological biochemical water purification device
CN101157498A (en) * 2007-09-18 2008-04-09 华东师范大学 Plant-Filler Biofilm Reactor
CN201746387U (en) * 2010-06-09 2011-02-16 江苏裕隆环保有限公司 Polluted water body in-situ repairing and purifying device
CN102079576B (en) * 2010-12-14 2012-12-19 上海师范大学 Surface water protection and remediation floating bioreactor and using method thereof
CN202625933U (en) * 2012-04-18 2012-12-26 清华大学深圳研究生院 Solar energy water body remedying and landscaping device in floating island form
CN203625129U (en) * 2013-10-19 2014-06-04 深圳职业技术学院 Floating bed type alga removing and landscaping device

Also Published As

Publication number Publication date
CN104003527A (en) 2014-08-27

Similar Documents

Publication Publication Date Title
CN104003527B (en) A kind of polluted water body in-situ prosthetic device and method thereof
CN203845918U (en) Energy-saving emission-reducing type town sewage treatment system
CN205011567U (en) Biological wet land treatment system of domestic sewage
CN204824550U (en) A device for rural domestic sewage treatment
CN102701448B (en) Rural domestic sewage reutilization treatment device
CN105502828A (en) Oligodynamic in-situ ecological restoration method of urban beheaded river
CN106045055A (en) Ecological restoration device and method for urban black-odor riverway
CN105906047A (en) Integrated water body in-situ remediation equipment and application thereof
CN202558739U (en) Rural life wastewater resource processing device
CN103304111A (en) Water network hill area village sewage collection treatment system
CN110104877A (en) A kind of artificial ecology wet land system handling cesspool sewage
CN104098223B (en) A kind of rural scattered domestic sewage processing system and method
CN105130123A (en) Northern residential district sewage processing system and method
CN203021357U (en) Assembly type river water purifying device for enhancing sand sedimentation by means of physical and ecological synergy
CN205382060U (en) Villages and small towns domestic sewage ecologization oligodynamic treatment system
CN105692876B (en) Using gravel as the buried ecological wastewater treatment system of medium and method
CN205368052U (en) Ecological wet land treatment system of dirty waste water low energy consumption in rural area compact community
CN110790451A (en) Black odorous water treatment system and method for treating black odorous water by using same
CN207567073U (en) A kind of garbage incinerating power plant sewage recycling effective utilization system
CN201704174U (en) Strengthened undercurrent artificial wetland
CN205035137U (en) Point source sewage treatment plant
CN208802963U (en) A siphon-type three-section decentralized sewage treatment system
Xu et al. Treat Phoenix River water by constructed rapid Infiltration system
CN207130118U (en) Packaged type sewage disposal system based on NW DMBR techniques
CN110790450B (en) River channel black and odorous water multistage repairing system and method

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20160120

Termination date: 20160606