CN114590905A - An integrated constructed wetland wastewater treatment system - Google Patents
An integrated constructed wetland wastewater treatment system Download PDFInfo
- Publication number
- CN114590905A CN114590905A CN202210451137.3A CN202210451137A CN114590905A CN 114590905 A CN114590905 A CN 114590905A CN 202210451137 A CN202210451137 A CN 202210451137A CN 114590905 A CN114590905 A CN 114590905A
- Authority
- CN
- China
- Prior art keywords
- wetland
- purification
- wastewater
- environment
- evaluation
- 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.)
- Granted
Links
- 238000004065 wastewater treatment Methods 0.000 title claims abstract description 30
- 238000000746 purification Methods 0.000 claims abstract description 144
- 239000002351 wastewater Substances 0.000 claims abstract description 139
- 230000007613 environmental effect Effects 0.000 claims abstract description 27
- 238000007689 inspection Methods 0.000 claims abstract description 12
- 238000004458 analytical method Methods 0.000 claims abstract description 8
- 238000011156 evaluation Methods 0.000 claims description 59
- 239000010802 sludge Substances 0.000 claims description 54
- 230000006978 adaptation Effects 0.000 claims description 19
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 17
- 229910052760 oxygen Inorganic materials 0.000 claims description 17
- 239000001301 oxygen Substances 0.000 claims description 17
- 238000005192 partition Methods 0.000 claims description 16
- 239000007921 spray Substances 0.000 claims description 14
- 238000004140 cleaning Methods 0.000 claims description 13
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 11
- 238000004062 sedimentation Methods 0.000 claims description 10
- 238000011002 quantification Methods 0.000 claims description 8
- 238000001556 precipitation Methods 0.000 claims description 7
- 230000008021 deposition Effects 0.000 claims description 6
- 238000006243 chemical reaction Methods 0.000 claims description 4
- 238000000034 method Methods 0.000 abstract description 7
- 230000008569 process Effects 0.000 abstract description 6
- 238000012545 processing Methods 0.000 abstract description 4
- 230000005540 biological transmission Effects 0.000 abstract description 3
- 239000002910 solid waste Substances 0.000 description 9
- 230000007423 decrease Effects 0.000 description 4
- 230000008635 plant growth Effects 0.000 description 4
- 238000003912 environmental pollution Methods 0.000 description 3
- 230000007774 longterm Effects 0.000 description 3
- 239000010865 sewage Substances 0.000 description 3
- 241001148470 aerobic bacillus Species 0.000 description 2
- 238000012937 correction Methods 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 239000007788 liquid Substances 0.000 description 2
- 238000013139 quantization Methods 0.000 description 2
- 238000004064 recycling Methods 0.000 description 2
- 239000007787 solid Substances 0.000 description 2
- 241001465754 Metazoa Species 0.000 description 1
- 238000009825 accumulation Methods 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 238000004364 calculation method Methods 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 230000007547 defect Effects 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 230000014759 maintenance of location Effects 0.000 description 1
- 230000010534 mechanism of action Effects 0.000 description 1
- 230000000813 microbial effect Effects 0.000 description 1
- 244000005700 microbiome Species 0.000 description 1
- 235000021231 nutrient uptake Nutrition 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 230000000243 photosynthetic effect Effects 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 230000029058 respiratory gaseous exchange Effects 0.000 description 1
- 229920006395 saturated elastomer Polymers 0.000 description 1
- 238000007790 scraping Methods 0.000 description 1
- 239000013049 sediment Substances 0.000 description 1
- 238000004088 simulation Methods 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 238000001179 sorption measurement Methods 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 230000009466 transformation Effects 0.000 description 1
- 230000005068 transpiration Effects 0.000 description 1
- 241001148471 unidentified anaerobic bacterium Species 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
Images
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/32—Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/30—Aerobic and anaerobic processes
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2203/00—Apparatus and plants for the biological treatment of water, waste water or sewage
- C02F2203/006—Apparatus and plants for the biological treatment of water, waste water or sewage details of construction, e.g. specially adapted seals, modules, connections
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2303/00—Specific treatment goals
- C02F2303/14—Maintenance of water treatment installations
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Engineering & Computer Science (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)
- Biotechnology (AREA)
- Botany (AREA)
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
Abstract
本发明公开了一种整体式人工湿地废水处理系统,涉及人工湿地技术领域,本发明通过设置湿地废水处理单元、湿地信息采集单元、湿地基础运检单元、湿地深度运行单元和文本编辑单元,在使废水在湿地处进行自流动净化的基础上,通过对湿地处环境参数的信息采集、分析、对比和处理,并配合采集湿地净化能力,从而实现湿地处环境参数与湿地净化能力有机结合,使湿地达到最佳饱和状态,从而提高净化的效率和能力,解决了传统湿地无法对环境参数进行检测并处理,无法使湿地的净化处于实时饱和状态,造成传动湿地净化处理效率较低的问题。
The invention discloses an integrated constructed wetland wastewater treatment system, which relates to the technical field of constructed wetlands. The present invention provides a wetland wastewater treatment unit, a wetland information collection unit, a wetland basic inspection unit, a wetland depth operation unit and a text editing unit. On the basis of the self-flow purification of wastewater in the wetland, through the information collection, analysis, comparison and processing of the environmental parameters of the wetland, and the collection of the wetland purification capacity, the organic combination of the environmental parameters of the wetland and the purification capacity of the wetland can be achieved. The wetland reaches the optimal saturation state, thereby improving the efficiency and ability of purification, solving the problem that traditional wetlands cannot detect and process environmental parameters, and cannot make the purification of wetlands in a real-time saturation state, resulting in low efficiency of transmission wetland purification.
Description
技术领域technical field
本发明涉及人工湿地技术领域,尤其涉及一种整体式人工湿地废水处理系统。The invention relates to the technical field of constructed wetlands, and in particular to an integrated constructed wetland wastewater treatment system.
背景技术Background technique
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;Constructed wetlands are artificially constructed and controlled grounds similar to swamps. Sewage and sludge are distributed on the artificially constructed wetlands in a controlled manner. In the process of flowing in a certain direction, sewage and sludge are mainly used. The physical, chemical, and biological triple synergy of soil, artificial media, plants, and microorganisms is a technology for the treatment of sewage and sludge. Its mechanism of action includes adsorption, retention, filtration, redox, precipitation, microbial decomposition, transformation, Plant shading, residue accumulation, transpiration water and nutrient uptake and the role of various animals;
其中公开号为CN206814493U4的人工湿地废水处理系统通过整体腔室的设置能够有效地控制占地面积,首先根据整体腔室的大小来规划分池体的大小,能够很好地进行占地面积的控制,提高空间的利用率,但是其还存在一些不足之处,其湿地无法对环境参数进行检测并处理,无法使湿地的净化处于实时饱和状态,造成湿地净化处理效率较低,且当湿地进行长时间运作时,淤泥会被湿地植物吸收消耗一部分,但是湿地还是会沉淀大量的淤泥,由于其沉淀在湿地植物处,因此在清理时,会破坏湿地植物,而湿地植物的根系牢牢抓住淤泥,使清洁湿地淤泥较为困难,当淤泥沉淀到一定程度时,使废水易于流出,还会造成环境污染;Among them, the constructed wetland wastewater treatment system with the publication number of CN206814493U4 can effectively control the floor space through the setting of the overall chamber. First, the size of the sub-pools is planned according to the size of the overall chamber, which can well control the floor space. , to improve the utilization rate of space, but it still has some shortcomings. The wetland cannot detect and process environmental parameters, and cannot make the wetland purification in a real-time saturation state, resulting in low efficiency of wetland purification and treatment, and when the wetland is long-term When the time is running, the silt will be absorbed and consumed by the wetland plants, but a large amount of silt will still be deposited in the wetland. Since it is deposited in the wetland plants, it will destroy the wetland plants during cleaning, and the roots of the wetland plants will firmly grasp the silt. , it is more difficult to clean the wetland sludge, when the sludge settles to a certain extent, the waste water is easy to flow out, and it will also cause environmental pollution;
针对上述的技术缺陷,现提出一种解决方案。Aiming at the above-mentioned technical defects, a solution is proposed.
发明内容SUMMARY OF THE INVENTION
本发明的目的在于:通过设置湿地废水处理单元、湿地信息采集单元、湿地基础运检单元、湿地深度运行单元和文本编辑单元,在使废水在湿地处进行自流动净化的基础上,通过对湿地处环境参数的信息采集、分析、对比和处理,并配合采集湿地净化能力,从而实现湿地处环境参数与湿地净化能力有机结合,使湿地达到最佳饱和状态,从而提高净化的效率和能力;在实现湿地废水自流动净化处理的基础上,通过种植在等比种植台的植物对湿地废水内的固态废物进行多次分解,然后由于湿地废水自流动的作用,将分解后的固态废物进行逐级沉淀汇集到指定区,然后通过设置超声波传感器、喷洒清洁组件、地管和自吸输送器将达到沉淀高度的淤泥进行扬起、打散、吸取、回收,从而实现了湿地的固态废物回收工作,保证工作的持续进行;The purpose of the present invention is: by setting up a wetland wastewater treatment unit, a wetland information collection unit, a wetland basic inspection unit, a wetland depth operation unit and a text editing unit, on the basis of making the wastewater self-flow purification in the wetland, Information collection, analysis, comparison and processing of environmental parameters at the site, and cooperate with the collection of wetland purification capabilities, so as to realize the organic combination of wetland environment parameters and wetland purification capabilities, so that the wetland can reach the best saturation state, thereby improving the efficiency and ability of purification; On the basis of realizing the self-flow purification treatment of wetland wastewater, the solid waste in the wetland wastewater is decomposed multiple times by the plants planted on the planting platform of equal ratio, and then the decomposed solid waste is gradually decomposed due to the self-flow of the wetland wastewater. The sediment is collected in the designated area, and then the sludge that has reached the sedimentation height is lifted, scattered, sucked and recycled by setting up ultrasonic sensors, spray cleaning components, ground pipes and self-priming conveyors, thus realizing the solid waste recovery of wetlands. ensure the continuation of work;
为了实现上述目的,本发明采用了如下技术方案:In order to achieve the above object, the present invention adopts the following technical solutions:
一种整体式人工湿地废水处理系统,包括:An integral constructed wetland wastewater treatment system, comprising:
湿地废水处理单元,用于湿地自流动湿地废水净化的工作;Wetland wastewater treatment unit, used for the purification of wetland self-flowing wetland wastewater;
湿地信息采集单元,用于采集湿地废水净化环境信息和湿地淤泥沉淀信息并将其发送给湿地基础运检单元;Wetland information collection unit, used to collect wetland wastewater purification environmental information and wetland sludge sedimentation information and send it to the wetland foundation inspection unit;
湿地基础运检单元,用于接收湿地废水净化环境信息和湿地淤泥沉淀信息并进基础分析模型得到湿地整体环境瞬时净化因子和湿地废水瞬时净化量,还将湿地废水瞬时净化量与预设值进行比较,当湿地废水瞬时净化量>预设值时,则不产生控制信号,反之,则产生立即控制进水量大小的第二控制信号;The wetland basic inspection unit is used to receive the wetland wastewater purification environmental information and the wetland sludge deposition information and enter into the basic analysis model to obtain the instantaneous purification factor of the overall wetland environment and the instantaneous purification amount of the wetland wastewater, and compare the instantaneous purification amount of the wetland wastewater with the preset value. , when the instantaneous purification amount of wetland wastewater is greater than the preset value, no control signal is generated, otherwise, a second control signal that immediately controls the amount of water inflow is generated;
还将湿地整体环境瞬时净化因子与预设阈值进行比较并生成将湿地整体环境瞬时净化因子和湿地废水瞬时净化量发送给湿地深度运行单元的第一控制信号;Also compare the instantaneous purification factor of the overall wetland environment with the preset threshold, and generate a first control signal for sending the instantaneous purification factor of the overall wetland environment and the instantaneous purification amount of the wetland wastewater to the wetland deep operation unit;
湿地深度评测单元,用于接收湿地整体环境瞬时净化因子和湿地废水瞬时净化量并量化生成湿地环境净化饱和适配度,且将湿地环境净化饱和适配度与预期范围值进行比较并生成评估信号,且将评估信号发送给文本编辑单元;The wetland depth evaluation unit is used to receive the instantaneous purification factor of the overall wetland environment and the instantaneous purification amount of the wetland wastewater, quantify and generate the wetland environment purification saturation adaptation degree, and compare the wetland environment purification saturation adaptation degree with the expected range value and generate an evaluation signal , and send the evaluation signal to the text editing unit;
文本编辑单元,用于接收评估信号并立即编辑评估文本。Text editing unit for receiving evaluation signals and editing evaluation texts immediately.
进一步的,湿地废水净化环境信息由湿地废水区域范围内的外部平均温度、湿地废水区域范围内的内部平均温度、湿地废水区域范围内的植株总面积、湿地废水区域范围内的植株单位平均密度、湿地废水顶部含氧量和湿地废水底部含氧量构成;而湿地淤泥沉淀信息为湿地淤泥沉淀单位时间均高、湿地废水透明度和湿地废水进液量构成。Further, the environmental information of wetland wastewater purification includes the external average temperature within the wetland wastewater area, the internal average temperature within the wetland wastewater area, the total area of plants within the wetland wastewater area, the unit average density of plants within the wetland wastewater area, The oxygen content at the top of the wetland wastewater and the oxygen content at the bottom of the wetland wastewater are composed of; and the information on the sedimentation of the wetland sludge is composed of the high unit time of the wetland sludge precipitation, the transparency of the wetland wastewater, and the influent volume of the wetland wastewater.
进一步的,基础分析模型的具体工作步骤如下:Further, the specific working steps of the basic analysis model are as follows:
Sa:实时接收到湿地废水区域范围内的外部平均温度、湿地废水区域范围内的内部平均温度、湿地废水区域范围内的植株总面积、湿地废水区域范围内的植株单位平均密度、湿地废水顶部含氧量和湿地废水底部含氧量经处理得到湿地整体环境瞬时净化因子A;Sa: The average external temperature within the wetland wastewater area, the average internal temperature within the wetland wastewater area, the total plant area within the wetland wastewater area, the unit average density of plants within the wetland wastewater area, and the top content of the wetland wastewater are received in real time. The oxygen content and the oxygen content at the bottom of the wetland wastewater are treated to obtain the instantaneous purification factor A of the wetland overall environment;
然后将生成的湿地整体环境净化因子A与预设阈值a进行比较,当amin≤A<amax时,则不产生控制信号,反之,则产生第一控制信号;Then compare the generated wetland overall environmental purification factor A with the preset threshold value a, when amin≤A<amax, no control signal is generated, otherwise, a first control signal is generated;
Sb:将湿地淤泥沉淀单位时间均高、湿地废水透明度和湿地废水进液量将其分别标定为H、M和L,然后依据公式得到湿地废水瞬时净化量B,其中e7、e8和e9为瞬时量化因子;Sb: The average unit time of wetland sludge precipitation, the transparency of wetland wastewater and the amount of wetland wastewater inflow are calibrated as H, M and L respectively, and then according to the formula Obtain the instantaneous purification amount B of wetland wastewater, where e7, e8 and e9 are instantaneous quantification factors;
还将湿地废水瞬时净化量B与预设值b进行比较,当B>b时,则不产生控制信号,反之,则产生控制进水量的第二控制信号;The instantaneous purification amount B of the wetland wastewater is also compared with the preset value b, when B>b, no control signal is generated, otherwise, a second control signal for controlling the water intake is generated;
Sc:当生成第一控制信号时,将湿地整体环境瞬时净化因子A和湿地废水瞬时净化量B发送给湿地深度运行单元。Sc: When the first control signal is generated, the instantaneous purification factor A of the overall wetland environment and the instantaneous purification amount B of the wetland wastewater are sent to the wetland depth operation unit.
进一步的,湿地深度评测单元的具体工作步骤如下:Further, the specific working steps of the wetland depth evaluation unit are as follows:
湿地深度运行单元在接收到湿地整体环境瞬时净化因子A和湿地废水瞬时净化量B后将其储存并生成湿地整体环境净化历史因子和湿地废水历史净化量;After receiving the instantaneous purification factor A of the wetland overall environment and the instantaneous purification amount B of the wetland wastewater, the wetland deep operation unit stores them and generates the historical factor of wetland overall environmental purification and the historical purification amount of the wetland wastewater;
然后提取若干个湿地整体环境净化历史因子和湿地废水历史净化量分别计算得到第一目标量化标准差值AJ和第二目标量化标准差值BJ,通过第一目标量化标准差值AJ和第二目标量化标准差值BJ,经公式Zs=|AJ-BJ|/(AJ+BJ),得到湿地环境净化饱和适配度Zs;Then, several historical factors of wetland overall environmental purification and historical purification amount of wetland wastewater are extracted to obtain the first target quantification standard deviation value AJ and the second target quantification standard deviation value BJ, respectively. Quantify the standard deviation value BJ, through the formula Zs=|AJ-BJ|/(AJ+BJ), get the wetland environment purification saturation adaptation degree Zs;
还将湿地环境净化饱和适配度Zs与预期范围值zq进行比较,当zs=zq时,则产生非最佳净化环境下的第一评估信号;反之,则产生非最佳净化环境下的第二评估信号;The purification saturation adaptation degree Zs of the wetland environment is also compared with the expected range value zq. When zs=zq, the first evaluation signal under the non-optimal purification environment is generated; otherwise, the first evaluation signal under the non-optimal purification environment is generated. 2. Evaluation signal;
还将生成的湿地环境净化饱和适配度Zs、第一评估信号和第二评估信号发送给文本编辑单元。The generated wetland environment purification saturation adaptation degree Zs, the first evaluation signal and the second evaluation signal are also sent to the text editing unit.
进一步的,文本编辑单元的具体工作步骤如下:Further, the specific working steps of the text editing unit are as follows:
当文本编辑单元接收到湿地整体真实评价值zs和第一评估信号后立即编辑第一评估文本,第一评估文本为“在非最佳净化环境下湿地的湿地环境净化饱和适配度为Zs,此时湿地环境长期处于动态净化饱和状态”;When the text editing unit receives the overall real evaluation value zs of the wetland and the first evaluation signal, it immediately edits the first evaluation text, and the first evaluation text is "the wetland environment purification saturation adaptation degree of the wetland under the non-optimal purification environment is Zs, At this time, the wetland environment is in a state of dynamic purification and saturation for a long time”;
当文本编辑模块接收到湿地整体真实评价值zs和第二评估信号后立即编辑第二评估文本,第二评估文本为“在非最佳净化环境下湿地的湿地环境净化饱和适配度为Zs,此时湿地环境长期处于非动态净化饱和状态”;非最佳净化环境通常指较冷或较热引发的连锁反应;When the text editing module receives the overall real evaluation value zs of the wetland and the second evaluation signal, it immediately edits the second evaluation text, and the second evaluation text is "the wetland environment purification saturation adaptation degree of the wetland under the non-optimal purification environment is Zs, At this time, the wetland environment is in a state of non-dynamic purification and saturation for a long time”; the non-optimal purification environment usually refers to the chain reaction caused by colder or hotter;
且将编辑后的第一评估文本和第二评估文本发送到显示终端显示。And the edited first evaluation text and second evaluation text are sent to the display terminal for display.
进一步的,湿地废水处理单元包括湿地废水处理单元包括湿地底基,所述湿地底基对称设置,所述湿地底基的顶端安装有湿地围框,所述湿地底基设有等比种植台和等比隔板,所述等比隔板和等比隔板之间间隙配合构成淤泥汇聚槽,所述等比种植台和等比隔板均设有多个,且等比种植台和等比隔板呈一一对应关系,所述等比种植台和等比隔板的高度均等量依次变小,所述淤泥汇聚槽适配有喷洒清洁组件,所述淤泥汇聚槽的底端贯通连接有地管,所述地管的另一端贯通连接有自吸输送器,所述自吸输送器上安装有控制阀,所述湿地围框贯通连接有废水进口,所述废水进口安装有节流阀,所述湿地围框固定等距安装有若干个分叉支柱,所述分叉支柱上安装有超声波传感器和温度传感器。Further, the wetland wastewater treatment unit includes a wetland wastewater treatment unit including a wetland base, the wetland base is symmetrically arranged, a wetland enclosure is installed at the top of the wetland base, and the wetland base is provided with an equal-proportion planting platform and Equal-proportion clapboard, the gap between the equal-ratio clapboard and the equal-ratio clapboard constitutes a sludge gathering tank, the equal-ratio planting table and the equal-ratio clapboard are provided with multiple, and the equal-ratio planting table and the equal-ratio The partitions are in a one-to-one correspondence, the heights of the equal-proportion planting platform and the equal-proportion partition become smaller and smaller in turn, the sludge gathering tank is adapted to a spray cleaning component, and the bottom end of the sludge convergence tank is connected with A ground pipe, the other end of the ground pipe is connected with a self-priming conveyor, a control valve is installed on the self-priming conveyor, the wetland enclosure is connected with a waste water inlet, and a throttle valve is installed on the waste water inlet A plurality of bifurcated struts are fixed and equidistantly installed on the wetland enclosure, and an ultrasonic sensor and a temperature sensor are installed on the bifurcated struts.
进一步的,所述喷洒清洁组件包括支撑板,所述支撑板固定设于两个湿地围框之间,所述支撑板的顶面中心处固定设有往复电机,所述往复电机的输出轴固定连接有第一转杆,所述第一转杆的顶部固定套设与均衡盘,所述均衡盘的两端固定连接有L形空心杆,所述L形空心杆的内端与支撑板抵接,所述L形空心杆的外端固定连接有空心斜杆,所述L形空心杆与空心斜杆贯通连接,所述空心斜杆的外端固定连接有空心连接杆,所述空心连接杆等距设有多个,所述空心连接杆与空心斜杆贯通连接,且空心连接杆与淤泥汇聚槽的数量相等,所述空心连接杆远离空心斜杆的一端固定设有空心刮板,所述空心刮板的两侧开设有喷孔,所述空心刮板相邻喷孔的两侧与淤泥汇聚槽滑动抵接,所述空心刮板的底端与淤泥汇聚槽的底壁滑动抵接,空心连接杆与空心刮板贯通连接。Further, the spray cleaning assembly includes a support plate, the support plate is fixed between the two wetland enclosures, the center of the top surface of the support plate is fixed with a reciprocating motor, and the output shaft of the reciprocating motor is fixed. A first rotating rod is connected, the top of the first rotating rod is fixedly sleeved with the equalizing disc, and the two ends of the equalizing disc are fixedly connected with an L-shaped hollow rod, and the inner end of the L-shaped hollow rod is in contact with the support plate. The outer end of the L-shaped hollow rod is fixedly connected with a hollow inclined rod, the L-shaped hollow rod and the hollow inclined rod are throughly connected, and the outer end of the hollow inclined rod is fixedly connected with a hollow connecting rod, and the hollow connection There are a plurality of rods at equal distances, the hollow connecting rods and the hollow inclined rods are throughly connected, and the number of the hollow connecting rods and the silt gathering tanks is equal, and a hollow scraper is fixed at one end of the hollow connecting rods away from the hollow inclined rods, The two sides of the hollow scraper are provided with spray holes, the two sides of the adjacent spray holes of the hollow scraper are in sliding contact with the sludge collecting tank, and the bottom end of the hollow scraper is in sliding contact with the bottom wall of the sludge collecting tank. The hollow connecting rod is connected with the hollow scraper.
进一步的,所述自吸输送器由汇聚壳、第二转杆、螺纹旋叶和伺服电机构成,所述第二转杆转动设于汇聚壳内,所述螺纹旋叶固定套设于第二转杆的外端,所述汇聚壳与地管固定连接,所述伺服电机固定设于汇聚壳的一端,所述第二转杆的一端贯穿汇聚壳的内壁延伸到其外部并与伺服电机的输出轴固定连接,所述控制阀设于伺服电机的相对端。Further, the self-priming conveyor is composed of a converging casing, a second rotating rod, a threaded rotary blade and a servo motor, the second rotating rod is rotatably arranged in the converging casing, and the threaded rotating blade is fixedly sleeved on the second rotating blade. At the outer end of the rotating rod, the converging shell is fixedly connected to the ground pipe, the servo motor is fixed on one end of the converging shell, and one end of the second rotating rod extends through the inner wall of the converging shell to the outside thereof and is connected with the servo motor. The output shaft is fixedly connected, and the control valve is arranged on the opposite end of the servo motor.
综上所述,由于采用了上述技术方案,本发明的有益效果是:To sum up, due to the adoption of the above-mentioned technical solutions, the beneficial effects of the present invention are:
1、本发明通过设置湿地废水处理单元、湿地信息采集单元、湿地基础运检单元、湿地深度运行单元和文本编辑单元,在使废水在湿地处进行自流动净化的基础上,通过对湿地处环境参数的信息采集、分析、对比和处理,并配合采集湿地净化能力,从而实现湿地处环境参数与湿地净化能力有机结合,使湿地达到最佳饱和状态,从而提高净化的效率和能力,解决了传统湿地无法对环境参数进行检测并处理,无法使湿地的净化处于实时饱和状态,造成传动湿地净化处理效率较低的问题;1. In the present invention, by setting up a wetland wastewater treatment unit, a wetland information collection unit, a wetland basic inspection unit, a wetland in-depth operation unit and a text editing unit, on the basis of making the wastewater self-flowing and purifying in the wetland, through the wetland environment Information collection, analysis, comparison and processing of parameters, and cooperate with the collection of wetland purification capacity, so as to realize the organic combination of wetland environmental parameters and wetland purification capacity, so that the wetland can reach the best saturation state, thereby improving the efficiency and capacity of purification, solving the traditional problem. The wetland cannot detect and process the environmental parameters, and the purification of the wetland cannot be in a real-time saturation state, resulting in the problem of low efficiency of transmission wetland purification;
2、本发明在实现湿地废水自流动净化处理的基础上,通过种植在等比种植台的植物对湿地废水内的固态废物进行多次分解,然后由于湿地废水自流动的作用,将分解后的固态废物进行逐级沉淀汇集到指定区,然后通过设置超声波传感器、喷洒清洁组件、地管和自吸输送器将达到沉淀高度的淤泥进行扬起、打散、吸取、回收,从而实现了湿地的固态废物回收工作,保证工作的持续进行,解决了传统湿地当长时间运作后,造成淤泥沉淀较高,不便于清理,易造成环境污染的问题。2. On the basis of realizing the self-flow purification treatment of wetland wastewater, the present invention decomposes the solid waste in the wetland wastewater multiple times through plants planted on a proportional planting platform. The solid waste is gradually deposited and collected into the designated area, and then the sludge that has reached the sedimentation height is lifted, scattered, sucked, and recycled by setting ultrasonic sensors, spray cleaning components, ground pipes and self-priming conveyors, thereby realizing the wetland. The solid waste recycling work ensures the continuous operation of the work, and solves the problem of high sludge sedimentation caused by traditional wetlands after long-term operation, which is inconvenient for cleaning and easy to cause environmental pollution.
附图说明Description of drawings
图1示出了本发明的流程框图;Fig. 1 shows the flow chart of the present invention;
图2示出了湿地废水处理单元的示意图;Figure 2 shows a schematic diagram of a wetland wastewater treatment unit;
图3示出了湿地废水处理单元的局部剖面图;Figure 3 shows a partial cross-sectional view of the wetland wastewater treatment unit;
图4示出了图2的A处局部放大图;Fig. 4 shows a partial enlarged view at A of Fig. 2;
图5示出了自吸输送器的结构示意图;Figure 5 shows a schematic structural diagram of a self-priming conveyor;
图例说明:1、湿地底基;2、湿地围框;3、等比种植台;4、等比隔板;5、淤泥汇聚槽;6、喷洒清洁组件;7、地管;8、自吸输送器;9、废水进口;10、节流阀;11、分叉支柱;12、超声波传感器;13、温度传感器;14、控制阀;601、支撑板;602、往复电机;603、第一转杆;604、均衡盘;605、L形空心杆;606、空心斜杆;607、空心连接杆;608、空心刮板;609、喷孔;801、汇聚壳;802、第二转杆;803、螺纹旋叶;804、伺服电机。Legend: 1. Wetland base; 2. Wetland enclosure; 3. Equal-proportion planting platform; 4. Equal-proportion partition; Conveyor; 9. Wastewater inlet; 10. Throttle valve; 11. Bifurcated strut; 12. Ultrasonic sensor; 13. Temperature sensor; 14. Control valve; 601, Support plate; 602, Reciprocating motor; 603, First turn Rod; 604, equalizing disc; 605, L-shaped hollow rod; 606, hollow inclined rod; 607, hollow connecting rod; 608, hollow scraper; 609, nozzle hole; 801, convergence shell; 802, second rotating rod; 803 , Threaded rotor; 804, servo motor.
具体实施方式Detailed ways
下面将结合本发明实施例中的附图,对本发明实施例中的技术方案进行清楚、完整地描述,显然,所描述的实施例仅仅是本发明一部分实施例,而不是全部的实施例。基于本发明中的实施例,本领域普通技术人员在没有作出创造性劳动前提下所获得的所有其它实施例,都属于本发明保护的范围。The technical solutions in the embodiments of the present invention will be clearly and completely described below with reference to the accompanying drawings in the embodiments of the present invention. Obviously, the described embodiments are only a part of the embodiments of the present invention, but not all of the embodiments. Based on the embodiments of the present invention, all other embodiments obtained by those of ordinary skill in the art without creative efforts shall fall within the protection scope of the present invention.
实施例1:Example 1:
如图1所示,一种整体式人工湿地废水处理系统,包括湿地废水处理单元、湿地信息采集单元、湿地基础运检单元、湿地深度运行单元和文本编辑单元;As shown in Figure 1, an integrated constructed wetland wastewater treatment system includes a wetland wastewater treatment unit, a wetland information collection unit, a wetland basic inspection unit, a wetland depth operation unit, and a text editing unit;
湿地废水处理单元,用于湿地自流动净化湿地废水;Wetland wastewater treatment unit, used for wetland self-flow purification of wetland wastewater;
湿地信息采集单元,用于采集湿地废水净化环境信息和湿地淤泥沉淀信息并将其发送给湿地基础运检单元;Wetland information collection unit, used to collect wetland wastewater purification environmental information and wetland sludge sedimentation information and send it to the wetland foundation inspection unit;
其中湿地废水净化环境信息由湿地废水区域范围内的外部平均温度、湿地废水区域范围内的内部平均温度、湿地废水区域范围内的植株总面积、湿地废水区域范围内的植株单位平均密度、湿地废水顶部含氧量和湿地废水底部含氧量构成;The environmental information of wetland wastewater purification includes the external average temperature within the wetland wastewater area, the internal average temperature within the wetland wastewater area, the total plant area within the wetland wastewater area, the average density of plants per unit within the wetland wastewater area, and the wetland wastewater area. The oxygen content at the top and the oxygen content at the bottom of the wetland wastewater are composed;
湿地废水区域范围内的外部平均温度的升降会影响湿地废水区域范围内的内部平均温度的升降,湿地废水区域范围内的内部平均温度的升降会影响湿地环境内植株的生长,从而影响湿地废水区域范围内的植株总面积和湿地废水区域范围内的植株单位平均密度,当温度较高和较低均会影响湿地环境内植株的生长,而湿地环境内植株的生长会产生或消耗氧气,从而影响到湿地废水内的含氧量,含氧量的大小显然会影响到好氧菌或厌氧菌的多少,好氧菌生活在湿地废水的顶部,因此采集湿地废水顶部含氧量,厌氧菌生长在湿地废水的底部,因此湿地废水底部的含氧量,因此在湿地废水顶部种植光合作用的植物,在湿地废水底部种植呼吸作用的植物,且需要其根系发达,使根系更好捕捉分解废水内固体颗粒;The rise and fall of the external average temperature within the wetland wastewater area will affect the rise and fall of the internal average temperature within the wetland wastewater area, and the rise and fall of the internal average temperature within the wetland wastewater area will affect the growth of plants in the wetland environment, thereby affecting the wetland wastewater area. The total plant area within the range and the average density of plants within the wetland wastewater area range. When the temperature is high and low, it will affect the growth of plants in the wetland environment, and the growth of plants in the wetland environment will produce or consume oxygen, thereby affecting the growth of plants. To the oxygen content in the wetland wastewater, the size of the oxygen content will obviously affect the number of aerobic bacteria or anaerobic bacteria. The aerobic bacteria live on the top of the wetland wastewater, so the oxygen content at the top of the wetland wastewater is collected. It grows at the bottom of wetland wastewater, so there is oxygen content at the bottom of wetland wastewater. Therefore, photosynthetic plants are planted on the top of wetland wastewater, and respiration plants are planted at the bottom of wetland wastewater, and its root system needs to be developed, so that the root system can better capture and decompose wastewater. Internal solid particles;
其中湿地淤泥沉淀信息为湿地淤泥沉淀单位时间均高、湿地废水透明度和湿地废水进液量构成;Among them, the wetland sludge deposition information is composed of the high unit time of wetland sludge deposition, the transparency of wetland wastewater, and the influent volume of wetland wastewater;
在湿地净化能力达到饱和后,其湿地废水进液量越多,其湿地净化固淤泥的能力就越差,湿地废水透明度就较低,造成其净化效果较差;因此需要通过湿地淤泥沉淀单位时间均高、湿地废水透明度和湿地废水进液量来整体性判断是否达到湿地净化饱和度;After the wetland purification capacity reaches saturation, the more the wetland wastewater enters the liquid, the worse the wetland purification ability of solid silt, and the lower the transparency of the wetland wastewater, resulting in a poor purification effect; therefore, it is necessary to pass the wetland sludge precipitation unit time The average height, the transparency of the wetland wastewater and the liquid inflow volume of the wetland wastewater can be used to judge whether the wetland purification saturation has been reached as a whole;
湿地基础运检单元的具体工作步骤如下:The specific working steps of the wetland foundation inspection unit are as follows:
湿地基础计算单元实时接收到湿地废水区域范围内的外部平均温度、湿地废水区域范围内的内部平均温度、湿地废水区域范围内的植株总面积、湿地废水区域范围内的植株单位平均密度、湿地废水顶部含氧量和湿地废水底部含氧量将其分别标定为Wa、Wb、Qa、Qb、Ca和Cb,然后依据公式得到湿地整体环境瞬时净化因子A;其中e1、e2、e3、e4、e5和e6为权重修正系数,权重修正系数使模拟计算的结果更加的接近真实值,e1>e2>e3>e4>e5>e6,e1+e2+e3+e4+e5+e6=34.16;The wetland basic computing unit receives in real time the average external temperature within the wetland wastewater area, the internal average temperature within the wetland wastewater area, the total area of plants within the wetland wastewater area, the unit average density of plants within the wetland wastewater area, and the wetland wastewater area. The oxygen content at the top and the oxygen content at the bottom of the wetland wastewater are respectively calibrated as Wa, Wb, Qa, Qb, Ca and Cb, and then according to the formula The instantaneous purification factor A of the wetland overall environment is obtained; in which e1, e2, e3, e4, e5 and e6 are the weight correction coefficients, and the weight correction coefficient makes the simulation calculation result closer to the real value, e1>e2>e3>e4>e5> e6, e1+e2+e3+e4+e5+e6=34.16;
其中湿地环境净化总体判断因子A,从环境相互关联性出发,以净化环境的整体性参数通过处理,从而实时检测出湿地整体性净化废水的效率和能力;Among them, the overall judgment factor A of wetland environment purification starts from the interrelatedness of the environment and processes the overall parameters of the purification environment, so as to detect the efficiency and ability of the wetland to purify the wastewater as a whole in real time;
还将生成的湿地整体环境净化因子A与预设阈值a进行比较,当amin≤A<amax时,则不产生控制信号,反之,则产生第一控制信号;The generated wetland overall environmental purification factor A is also compared with the preset threshold value a, when amin≤A<amax, no control signal is generated, otherwise, a first control signal is generated;
第一控制信号的产生说明环境使湿地整体净化能力变差,说明湿地处于非最佳净化环境下;The generation of the first control signal indicates that the environment makes the overall purification capability of the wetland worse, indicating that the wetland is in a non-optimal purification environment;
当湿地基础运检单元实时接收到湿地淤泥沉淀单位时间均高、湿地废水透明度和湿地废水进液量将其分别标定为H、M和L,然后依据公式得到湿地废水瞬时净化量B,其中e7、e8和e9为瞬时量化因子,瞬时量化因子使计算的结果更加的接近真实值,e9>e8>e7,且e9+e8+e7=7.81;When the wetland foundation inspection unit receives in real time that the wetland sludge sedimentation unit time is high, the transparency of wetland wastewater and the inflow volume of wetland wastewater, it will be calibrated as H, M and L respectively, and then according to the formula Obtain the instantaneous purification amount B of wetland wastewater, where e7, e8 and e9 are instantaneous quantization factors, and the instantaneous quantization factor makes the calculated result closer to the real value, e9>e8>e7, and e9+e8+e7=7.81;
还将湿地废水瞬时净化量B与预设值b进行比较,当B>b时,则不产生控制信号,反之,则产生第二控制信号;第二控制信号产生后立即降低进水量,增加拉长处理废水的时间,直到湿地废水瞬时净化量B>预设值b,使废水净化达到最佳;The instantaneous purification amount B of wetland wastewater is also compared with the preset value b. When B>b, no control signal is generated, otherwise, a second control signal is generated; immediately after the second control signal is generated, the water inflow is reduced and the pull rate is increased. Long time for wastewater treatment, until the instantaneous purification amount of wetland wastewater B > preset value b, so as to achieve the best wastewater purification;
其中产生第二控制信号则说明超过湿地瞬时净化能力,造成其废水透明度快速降低,其中湿地废水透明度0<M<1,且废水透明度越高,说明湿地废水越清澈,净化能力越好;The generation of the second control signal indicates that the instantaneous purification capacity of the wetland is exceeded, resulting in a rapid decrease in the transparency of the wastewater, where the transparency of the wetland wastewater is 0 < M < 1, and the higher the transparency of the wastewater, the clearer the wetland wastewater and the better the purification capacity;
当生成第一控制信号时,将湿地整体环境瞬时净化因子A和湿地废水瞬时净化量B发送给湿地深度运行单元;When the first control signal is generated, the instantaneous purification factor A of the overall wetland environment and the instantaneous purification amount B of the wetland wastewater are sent to the wetland deep operation unit;
湿地深度评测单元的具体工作步骤如下:The specific working steps of the wetland depth evaluation unit are as follows:
湿地深度运行单元接收到湿地整体环境瞬时净化因子A和湿地废水瞬时净化量B后将其储存并生成湿地整体环境净化历史因子和湿地废水历史净化量;The wetland in-depth operation unit receives the instantaneous purification factor A of the wetland overall environment and the instantaneous purification amount B of the wetland wastewater, and stores them to generate the historical factor of wetland overall environmental purification and the historical purification amount of the wetland wastewater;
然后提取若干个湿地整体环境净化历史因子和湿地废水历史净化量分别计算得到第一目标量化标准差值AJ和第二目标量化标准差值BJ,通过第一目标量化标准差值AJ和第二目标量化标准差值BJ,经公式Zs=|AJ-BJ|/(AJ+BJ),得到湿地环境净化饱和适配度Zs;Then, several historical factors of wetland overall environmental purification and historical purification amount of wetland wastewater are extracted to obtain the first target quantification standard deviation value AJ and the second target quantification standard deviation value BJ, respectively. Quantify the standard deviation value BJ, through the formula Zs=|AJ-BJ|/(AJ+BJ), get the wetland environment purification saturation adaptation degree Zs;
还将湿地环境净化饱和适配度Zs与预期范围值zq进行比较,当zs=zq时,则产生非最佳净化环境下的第一评估信号;反之,则产生非最佳净化环境下的第二评估信号;The purification saturation adaptation degree Zs of the wetland environment is also compared with the expected range value zq. When zs=zq, the first evaluation signal under the non-optimal purification environment is generated; otherwise, the first evaluation signal under the non-optimal purification environment is generated. 2. Evaluation signal;
还将生成的湿地环境净化饱和适配度Zs、第一评估信号和第二评估信号发送给文本编辑单元:The generated wetland environment purification saturation adaptation degree Zs, the first evaluation signal and the second evaluation signal are also sent to the text editing unit:
当文本编辑单元接收到湿地整体真实评价值zs和第一评估信号后立即编辑第一评估文本,第一评估文本为“在非最佳净化环境下湿地的湿地环境净化饱和适配度为Zs,此时湿地环境长期处于动态净化饱和状态”;When the text editing unit receives the overall real evaluation value zs of the wetland and the first evaluation signal, it immediately edits the first evaluation text, and the first evaluation text is "the wetland environment purification saturation adaptation degree of the wetland under the non-optimal purification environment is Zs, At this time, the wetland environment is in a state of dynamic purification and saturation for a long time”;
当文本编辑模块接收到湿地整体真实评价值zs和第二评估信号后立即编辑第二评估文本,第二评估文本为“在非最佳净化环境下湿地的湿地环境净化饱和适配度为Zs,此时湿地环境长期处于非动态净化饱和状态”;非最佳净化环境通常指较冷或较热引发的连锁反应;When the text editing module receives the overall real evaluation value zs of the wetland and the second evaluation signal, it immediately edits the second evaluation text, and the second evaluation text is "the wetland environment purification saturation adaptation degree of the wetland under the non-optimal purification environment is Zs, At this time, the wetland environment is in a state of non-dynamic purification and saturation for a long time”; the non-optimal purification environment usually refers to the chain reaction caused by colder or hotter;
且将编辑后的第一评估文本和第二评估文本发送到显示终端显示;And send the edited first evaluation text and the second evaluation text to the display terminal for display;
第二评估文本使工作人员适当的调整对应的应对措施,例如,适当的增减植株、增减温度等,保证非最佳净化环境下湿地处于饱和净化状态;The second evaluation text enables the staff to appropriately adjust the corresponding countermeasures, for example, appropriate increase or decrease of plants, increase or decrease of temperature, etc., to ensure that the wetland is in a saturated purification state in a non-optimal purification environment;
工作原理:本发明通过设置湿地废水处理单元、湿地信息采集单元、湿地基础运检单元、湿地深度运行单元和文本编辑单元,在使废水在湿地处进行自流动净化的基础上,通过对湿地处环境参数的信息采集、分析、对比和处理,并配合采集湿地净化能力,从而实现湿地处环境参数与湿地净化能力有机结合,使湿地达到最佳饱和状态,从而提高净化的效率和能力,解决了传统湿地无法对环境参数进行检测并处理,无法使湿地的净化处于实时饱和状态,造成传动湿地净化处理效率较低的问题。Working principle: The present invention sets up a wetland wastewater treatment unit, a wetland information collection unit, a wetland basic inspection unit, a wetland in-depth operation unit and a text editing unit. Information collection, analysis, comparison and processing of environmental parameters, and cooperate with the collection of wetland purification capacity, so as to realize the organic combination of wetland environmental parameters and wetland purification capacity, so that the wetland can reach the best saturation state, thereby improving the efficiency and capacity of purification, solving the problem of Traditional wetlands cannot detect and process environmental parameters, and cannot make the purification of wetlands in a real-time saturation state, resulting in the problem of low efficiency of transmission wetland purification.
实施例2:Example 2:
如图2-5所示,湿地废水处理单元包括湿地底基1,湿地底基1对称设置,湿地底基1的顶端安装有湿地围框2,湿地底基1和湿地围框2配合防止废水流出污染环境,湿地底基1设有等比种植台3和等比隔板4,等比隔板4和等比隔板4之间间隙配合构成淤泥汇聚槽5,等比种植台3和等比隔板4均设有多个,且等比种植台3和等比隔板4呈一一对应关系,等比种植台3和等比隔板4的高度均等量依次变小,等比隔板4用于限定废水的反应区域,等比种植台3用于种植不同的植株,通过将等比隔板4的高度等量依次变小形成高度差,实现废水的自流动,As shown in Figure 2-5, the wetland wastewater treatment unit includes a wetland base 1. The wetland base 1 is symmetrically arranged. A
淤泥汇聚槽5适配有喷洒清洁组件6,淤泥汇聚槽5的底端贯通连接有地管7,地管7的另一端贯通连接有自吸输送器8,喷洒清洁组件6用于刮擦淤泥汇聚槽5的底部,将其内沉淀的淤泥扬起,并喷洒清水,对其进行冲洗,然后自吸输送器8对淤泥进行吸取,使淤泥不会超过河床,导致废水流出,造成二次污染,自吸输送器8上安装有控制阀14,控制阀14用于关闭和打开清洁淤泥时的通路;The
湿地围框2贯通连接有废水进口9,废水进口9安装有节流阀10,节流阀10用于控制废水进入到湿地的量,湿地围框2固定等距安装有若干个分叉支柱11,分叉支柱11上安装有超声波传感器12和温度传感器13,超声波传感器12采集了整个湿地的三维立体图,湿地的三维立体图扫描出湿地淤泥沉淀高度,扫描出废水体内的杂质,废水内的杂质越多,其透明度就越低,扫描出植株在等比种植台3的面积和密度,温度传感器13用于感应外部环境温度,其他温度感应器分布于废水内,用于检测废水温度;The
喷洒清洁组件6包括支撑板601,支撑板601固定设于两个湿地围框2之间,支撑板601的顶面中心处固定设有往复电机602,往复电机602的输出轴固定连接有第一转杆603,第一转杆603的顶部固定套设与均衡盘604,均衡盘604的两端固定连接有L形空心杆605,L形空心杆605的内端与支撑板601抵接,L形空心杆605的外端固定连接有空心斜杆606,L形空心杆605与空心斜杆606贯通连接,空心斜杆606的底端与支撑板601的顶端滑动抵接,空心斜杆606的外端固定连接有空心连接杆607,空心连接杆607等距设有多个,空心连接杆607与空心斜杆606贯通连接,且空心连接杆607与淤泥汇聚槽5的数量相等,空心连接杆607远离空心斜杆606的一端固定设有空心刮板608,空心刮板608的两侧开设有喷孔609,空心刮板608相邻喷孔609的两侧与淤泥汇聚槽5滑动抵接,空心刮板608的底端与淤泥汇聚槽5的底壁滑动抵接,空心连接杆607与空心刮板608贯通连接;The
启动固定设于支撑板601中心处的往复电机602工作并控制其输出轴往复旋转,往复电机602的输出轴往复旋转后带动与其固定的第一转杆603往复旋转,第一转杆603往复旋转后带动与其固定套设的均衡盘604往复旋转,均衡盘604往复旋转后带动对称固定的两个L形空心杆605往复旋转,两个L形空心杆605此时沿湿地围框2做往复定弧长偏转,使L形空心杆605往复定弧长偏转得更加稳定均衡,L形空心杆605往复定弧长偏转后带动与其固定的空心斜杆606在等比隔板4的顶面往复滑动,空心斜杆606往复滑动后带动与其通过空心连接杆607固定的空心刮板608沿淤泥汇聚槽5做往复滑动,对淤泥汇聚槽5的底面进行刮擦,使淤泥汇聚槽5的沉淀淤泥被扬起推动,且同时打开两个L形空心杆605通过管道外接的水源,使被施加高压的清水进到L形空心杆605内,然后从L形空心杆605依次进入到空心斜杆606、空心连接杆607和空心刮板608,然后清水从空心刮板608的喷孔609喷出,对淤泥进行水压打散,使其更易被吸取;The
自吸输送器8由汇聚壳801、第二转杆802、螺纹旋叶803和伺服电机804构成,第二转杆802转动设于汇聚壳801内,螺纹旋叶803固定套设于第二转杆802的外端,汇聚壳801与地管7固定连接,这里的地管7还可先汇聚为一条,然后再与汇聚壳801贯通连接,增强自吸输送器8的吸力,伺服电机804固定设于汇聚壳801的一端,第二转杆802的一端贯穿汇聚壳801的内壁延伸到其外部并与伺服电机804的输出轴固定连接,控制阀14设于伺服电机804的相对端,当淤泥被推动扬起打散后,打开控制阀14并启动伺服电机804工作,伺服电机804工作后其输出轴旋转并带动与其固定的第二转杆802旋转,第二转杆802旋转后带动与其固定套接的螺纹旋叶803旋转,螺纹旋叶803旋转后将进入汇聚壳801内的淤泥进行推出回收,当汇聚壳801内的淤泥被持续性推出后,其汇聚壳801内的淤泥变少,使汇聚壳801产生中空后产生负压吸力,汇聚壳801产生负压吸力后通过地管7吸取淤泥汇聚内被扬起打散后的淤泥,当淤泥持续性被收取时,高压清水还对淤泥汇聚槽5进行清洁;The self-priming
本发明在实现湿地废水自流动净化处理的基础上,通过种植在等比种植台3的植物对湿地废水内的固态废物进行多次分解,然后由于湿地废水自流动的作用,将分解后的固态废物进行逐级沉淀汇集到指定区,然后通过设置超声波传感器12、喷洒清洁组件6、地管7和自吸输送器8将达到沉淀高度的淤泥进行扬起、打散、吸取、回收,从而实现了湿地的固态废物回收工作,保证工作的持续进行,解决了传统湿地当长时间运作后,造成淤泥沉淀较高,不便于清理,易造成环境污染的问题。On the basis of realizing the self-flow purification treatment of wetland waste water, the present invention decomposes the solid waste in the wetland waste water for many times through the plants planted on the equal
以上所述,仅为本发明较佳的具体实施方式,但本发明的保护范围并不局限于此,任何熟悉本技术领域的技术人员在本发明揭露的技术范围内,根据本发明的技术方案及其发明构思加以等同替换或改变,都应涵盖在本发明的保护范围之内。The above description is only a preferred embodiment of the present invention, but the protection scope of the present invention is not limited to this. The equivalent replacement or change of the inventive concept thereof shall be included within the protection scope of the present invention.
Claims (8)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202210451137.3A CN114590905B (en) | 2022-04-27 | 2022-04-27 | An integrated constructed wetland wastewater treatment system |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202210451137.3A CN114590905B (en) | 2022-04-27 | 2022-04-27 | An integrated constructed wetland wastewater treatment system |
Publications (2)
Publication Number | Publication Date |
---|---|
CN114590905A true CN114590905A (en) | 2022-06-07 |
CN114590905B CN114590905B (en) | 2022-09-27 |
Family
ID=81811507
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN202210451137.3A Active CN114590905B (en) | 2022-04-27 | 2022-04-27 | An integrated constructed wetland wastewater treatment system |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN114590905B (en) |
Citations (16)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS6377597A (en) * | 1986-09-18 | 1988-04-07 | Toshiba Corp | Device for withdrawal of sludge from settling basin |
CN102101725A (en) * | 2011-01-11 | 2011-06-22 | 南京大学 | Multifunctional lake ecology restoration simulation device and use method as well as application |
CN102167446A (en) * | 2011-05-04 | 2011-08-31 | 中咨城建设计有限公司 | Artificial wetland and construction method thereof |
CN103175513A (en) * | 2013-03-01 | 2013-06-26 | 戴会超 | System and method for monitoring hydrology and water quality of river basin under influence of water projects based on Internet of Things |
CN103869767A (en) * | 2012-12-07 | 2014-06-18 | 波音公司 | Forest sensor deployment and monitoring system |
CN203833709U (en) * | 2014-05-15 | 2014-09-17 | 山东省鲁南工程技术研究院 | Module for realizing rapid ecological construction of constructed wetland |
CN104049066A (en) * | 2014-06-26 | 2014-09-17 | 中国环境科学研究院 | River water quality and biological monitoring system and method for irregularly-shaped region |
CN104556391A (en) * | 2014-12-31 | 2015-04-29 | 东莞市蓝天创达化工有限公司 | Artificial wetland purification method for wastewater |
CN104787898A (en) * | 2014-11-11 | 2015-07-22 | 宁波清川环保工程有限公司 | Ecological restoration method of river close to nature |
US20160120140A1 (en) * | 2014-05-12 | 2016-05-05 | Kevin John Stevens | Device for phyto-ecological monitoring |
CN106021884A (en) * | 2016-05-12 | 2016-10-12 | 武汉理工大学 | Neural network principle-based method for predicting effluent concentration of subsurface flow wetland |
CN109006111A (en) * | 2018-07-16 | 2018-12-18 | 雷学军 | The method of Ecological Civilization Construction |
CN109292928A (en) * | 2018-10-12 | 2019-02-01 | 水利部交通运输部国家能源局南京水利科学研究院 | A pre-circulation water purification device suitable for high-yield and clean-up wetlands |
CN109502752A (en) * | 2018-11-23 | 2019-03-22 | 武汉理工大学 | A kind of intelligent power saving running gear of green top formula sewage classification processing system |
CN111398548A (en) * | 2020-04-09 | 2020-07-10 | 中国水利水电科学研究院 | A prediction method of nitrogen and phosphorus concentration in surface flow wetland water based on plant action |
CN216039151U (en) * | 2021-08-26 | 2022-03-15 | 淮北师范大学 | Can wash constructed wetland structure of preventing blockking up automatically |
-
2022
- 2022-04-27 CN CN202210451137.3A patent/CN114590905B/en active Active
Patent Citations (16)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS6377597A (en) * | 1986-09-18 | 1988-04-07 | Toshiba Corp | Device for withdrawal of sludge from settling basin |
CN102101725A (en) * | 2011-01-11 | 2011-06-22 | 南京大学 | Multifunctional lake ecology restoration simulation device and use method as well as application |
CN102167446A (en) * | 2011-05-04 | 2011-08-31 | 中咨城建设计有限公司 | Artificial wetland and construction method thereof |
CN103869767A (en) * | 2012-12-07 | 2014-06-18 | 波音公司 | Forest sensor deployment and monitoring system |
CN103175513A (en) * | 2013-03-01 | 2013-06-26 | 戴会超 | System and method for monitoring hydrology and water quality of river basin under influence of water projects based on Internet of Things |
US20160120140A1 (en) * | 2014-05-12 | 2016-05-05 | Kevin John Stevens | Device for phyto-ecological monitoring |
CN203833709U (en) * | 2014-05-15 | 2014-09-17 | 山东省鲁南工程技术研究院 | Module for realizing rapid ecological construction of constructed wetland |
CN104049066A (en) * | 2014-06-26 | 2014-09-17 | 中国环境科学研究院 | River water quality and biological monitoring system and method for irregularly-shaped region |
CN104787898A (en) * | 2014-11-11 | 2015-07-22 | 宁波清川环保工程有限公司 | Ecological restoration method of river close to nature |
CN104556391A (en) * | 2014-12-31 | 2015-04-29 | 东莞市蓝天创达化工有限公司 | Artificial wetland purification method for wastewater |
CN106021884A (en) * | 2016-05-12 | 2016-10-12 | 武汉理工大学 | Neural network principle-based method for predicting effluent concentration of subsurface flow wetland |
CN109006111A (en) * | 2018-07-16 | 2018-12-18 | 雷学军 | The method of Ecological Civilization Construction |
CN109292928A (en) * | 2018-10-12 | 2019-02-01 | 水利部交通运输部国家能源局南京水利科学研究院 | A pre-circulation water purification device suitable for high-yield and clean-up wetlands |
CN109502752A (en) * | 2018-11-23 | 2019-03-22 | 武汉理工大学 | A kind of intelligent power saving running gear of green top formula sewage classification processing system |
CN111398548A (en) * | 2020-04-09 | 2020-07-10 | 中国水利水电科学研究院 | A prediction method of nitrogen and phosphorus concentration in surface flow wetland water based on plant action |
CN216039151U (en) * | 2021-08-26 | 2022-03-15 | 淮北师范大学 | Can wash constructed wetland structure of preventing blockking up automatically |
Non-Patent Citations (3)
Title |
---|
AUGUSTO DE OLIVEIRA BRUNOW VENTURA ET AL.: "A new empirical index for assessing the vulnerability of peri-urban mangroves", 《JOURNAL OF ENVIRONMENTAL MANAGEMENT》 * |
刘飞: "人工湿地生态工程水力学参数的设计", 《环境科学与管理》 * |
施溯帆: "基于水环境容量控制绿色生态城区水资源利用规划研究", 《中国优秀硕士学位论文全文数据库 工程科技Ⅱ辑》 * |
Also Published As
Publication number | Publication date |
---|---|
CN114590905B (en) | 2022-09-27 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN100537462C (en) | Water purification method and facilities for water without water source | |
CN101215069B (en) | Industrialization ecological treatment circulation utilization system for fish culture waste water | |
CN101653105B (en) | Water-saving marine fish culture water purification plant and method | |
CN205627332U (en) | Waste liquid treatment device of live pig plant | |
CN112841117A (en) | Water purification device for organic mandarin fish culture | |
CN114590905B (en) | An integrated constructed wetland wastewater treatment system | |
CN202881023U (en) | Efficient landfill leachate treatment device | |
CN112047499A (en) | Riverway water quality improving device and using method thereof | |
CN110818199A (en) | Distributed rural domestic sewage low energy consumption integrated treatment equipment | |
CN1837090A (en) | Biological treatment device for multilayer drawer type cultural water | |
CN104163528B (en) | Circulation high-efficiency water-saving system | |
CN107572672A (en) | A kind of water body ecological repairing device of solar powered micro- oxygen silk oxygenation activation | |
CN202379857U (en) | Wetland ecological treatment device for municipal domestic sewage | |
CN207811495U (en) | A kind of simple fishpond sewage disposal system | |
CN202099118U (en) | Subsurface flow wetland system for restoring micro-polluted water | |
CN102503037B (en) | Hydroponic plant and filter dam combined eutrophication water body ex-situ remediation system | |
CN212315860U (en) | Buried sewage treatment equipment | |
CN107698101A (en) | A kind of domestic sewage processing system | |
CN202322557U (en) | Hydroponic plant and filter dam combined eutrophic water body ex-situ remediation system | |
CN2555267Y (en) | Artificial nunja plants bed | |
CN208218628U (en) | A kind of efficient sewage treatment installation | |
CN207685082U (en) | A kind of low energy consumption sewage treating artificial wet land device | |
CN207016563U (en) | A kind of irrigation Water warfare artificial wet land system with ecological canal function | |
CN217810781U (en) | A water conservancy project ecological wall | |
CN221729409U (en) | A circulating water flow oxygen-enriched aquaculture equipment |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
GR01 | Patent grant | ||
GR01 | Patent grant |