CN114590905A - An integrated constructed wetland wastewater treatment system - Google Patents

An integrated constructed wetland wastewater treatment system Download PDF

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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
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wastewater
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CN114590905B (en
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刘飞
刘晴川
王健
王馨
张立超
祝鹏飞
王莉
许崇
王法鑫
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Huaibei Normal University
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    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/32Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/30Aerobic and anaerobic processes
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2203/00Apparatus and plants for the biological treatment of water, waste water or sewage
    • C02F2203/006Apparatus and plants for the biological treatment of water, waste water or sewage details of construction, e.g. specially adapted seals, modules, connections
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
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    • C02F2303/14Maintenance of water treatment installations
    • 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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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。

Figure 202210451137

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.

Figure 202210451137

Description

一种整体式人工湿地废水处理系统An integrated constructed wetland wastewater treatment system

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

Figure BDA0003618652340000031
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
Figure BDA0003618652340000031
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

Figure BDA0003618652340000081
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
Figure BDA0003618652340000081
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

Figure BDA0003618652340000091
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
Figure BDA0003618652340000091
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 wetland enclosure 2 is installed on the top of the wetland base 1. The wetland base 1 and the wetland enclosure 2 cooperate to prevent waste water. Out of the polluted environment, the wetland base 1 is provided with a proportional planting platform 3 and a proportional partition plate 4, and the gap between the proportional partition plate 4 and the proportional partition plate 4 constitutes a sludge gathering tank 5, and the proportional planting platform 3 and etc. There are multiple partitions 4, and the proportional planting table 3 and the proportional partition 4 are in a one-to-one correspondence. The plate 4 is used to limit the reaction area of the wastewater, and the proportional planting platform 3 is used to plant different plants. The height difference is formed by decreasing the height of the proportional partition plate 4 in turn, so as to realize the self-flow of the wastewater.

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 sludge collecting tank 5 is fitted with a spray cleaning component 6, the bottom end of the sludge collecting tank 5 is connected with a ground pipe 7, and the other end of the ground pipe 7 is connected with a self-priming conveyor 8, and the spray cleaning component 6 is used for scraping the sludge At the bottom of the converging tank 5, the sludge deposited in it is raised, and clean water is sprayed to rinse it, and then the self-priming conveyor 8 absorbs the sludge, so that the sludge will not exceed the river bed, causing waste water to flow out, causing secondary pollution , a control valve 14 is installed on the self-priming conveyor 8, and the control valve 14 is used to close and open the passage when cleaning the sludge;

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 wetland enclosure 2 is throughly connected with a waste water inlet 9, and a throttle valve 10 is installed at the waste water inlet 9. The throttle valve 10 is used to control the amount of waste water entering the wetland. , an ultrasonic sensor 12 and a temperature sensor 13 are installed on the bifurcated pillar 11. The ultrasonic sensor 12 collects a three-dimensional three-dimensional view of the entire wetland. The three-dimensional three-dimensional image of the wetland scans the wetland sludge sedimentation height and scans out the impurities in the wastewater. The more, the lower the transparency, the area and density of the plants on the planting platform 3 in equal proportions are scanned, the temperature sensor 13 is used to sense the external ambient temperature, and other temperature sensors are distributed in the wastewater to detect the temperature of the wastewater;

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 spray cleaning assembly 6 includes a support plate 601, the support plate 601 is fixed between the two wetland enclosures 2, the center of the top surface of the support plate 601 is fixed with a reciprocating motor 602, and the output shaft of the reciprocating motor 602 is fixedly connected with a first The rotating rod 603, the top of the first rotating rod 603 is fixedly sleeved with the equalizing disk 604, the two ends of the equalizing disk 604 are fixedly connected with an L-shaped hollow rod 605, and the inner end of the L-shaped hollow rod 605 is in contact with the support plate 601, and the L-shaped hollow rod 605 is in contact with the support plate 601. The outer end of the hollow rod 605 is fixedly connected with a hollow inclined rod 606. The L-shaped hollow rod 605 is connected with the hollow inclined rod 606 throughly. The bottom end of the hollow inclined rod 606 is in sliding contact with the top of the support plate 601. The outer end is fixedly connected with a hollow connecting rod 607, and a plurality of hollow connecting rods 607 are arranged at equal distances. The hollow connecting rod 607 is connected with the hollow oblique rod 606 throughly, and the number of the hollow connecting rod 607 and the sludge gathering tank 5 is equal. The end of 607 away from the hollow inclined rod 606 is fixedly provided with a hollow scraper 608. The two sides of the hollow scraper 608 are provided with spray holes 609. The bottom end of the hollow scraper 608 is in sliding contact with the bottom wall of the sludge gathering tank 5, and the hollow connecting rod 607 is connected through the hollow scraper 608;

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 reciprocating motor 602 fixed at the center of the support plate 601 is started to work and the output shaft of the reciprocating motor 602 is controlled to reciprocate. After the reciprocating rotation of the output shaft of the reciprocating motor 602, the reciprocating rotation of the output shaft of the reciprocating motor 602 drives the first rotating rod 603 fixed to it to rotate back and forth, and the first rotating rod 603 rotates back and forth. Afterwards, it drives the equalizing disc 604 that is fixedly sleeved with it to reciprocate. The equalizing disc 604 reciprocates and drives the two L-shaped hollow rods 605 that are symmetrically fixed to reciprocate. At this time, the two L-shaped hollow rods 605 reciprocate along the wetland enclosure 2 The arc length is deflected, so that the reciprocating and fixed arc length deflection of the L-shaped hollow rod 605 is more stable and balanced. After the L-shaped hollow rod 605 is deflected in a reciprocating and fixed arc length, it drives the hollow inclined rod 606 fixed to it to slide back and forth on the top surface of the equal-proportion partition 4 After the hollow inclined rod 606 slides back and forth, it drives the hollow scraper 608 fixed by the hollow connecting rod 607 to slide back and forth along the sludge collecting tank 5, and scrape the bottom surface of the sludge collecting tank 5, so that the sedimented sludge in the sludge collecting tank 5 is removed. Raise and push, and simultaneously open the two L-shaped hollow rods 605 through the external water source of the pipeline, so that the high-pressure clean water enters the L-shaped hollow rod 605, and then enters the hollow inclined rod 606, The hollow connecting rod 607 and the hollow scraper 608, and then clean water is sprayed from the nozzle hole 609 of the hollow scraper 608, and the sludge is dispersed by water pressure, making it easier to be absorbed;

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 conveyor 8 is composed of a converging casing 801, a second rotating rod 802, a threaded rotating blade 803 and a servo motor 804. The second rotating rod 802 is rotatably installed in the converging casing 801, and the threaded rotating blade 803 is fixedly sleeved on the second rotating rod 801. At the outer end of the rod 802, the converging shell 801 is fixedly connected with the ground pipe 7. Here, the ground pipe 7 can also be converged into one piece, and then connected with the converging shell 801 to enhance the suction force of the self-priming conveyor 8. The servo motor 804 is fixed Set at one end of the converging shell 801, one end of the second rotating rod 802 extends through the inner wall of the converging shell 801 to the outside thereof and is fixedly connected with the output shaft of the servo motor 804. The control valve 14 is set at the opposite end of the servo motor 804. After being pushed up and scattered, open the control valve 14 and start the servo motor 804 to work. After the servo motor 804 works, its output shaft rotates and drives the second rotating rod 802 fixed to it to rotate. After the second rotating rod 802 rotates, it drives it to be fixed. The socketed threaded rotary vane 803 rotates. After the threaded rotary vane 803 rotates, it pushes out and recycles the sludge that enters the converging shell 801. When the sludge in the converging shell 801 is continuously pushed out, the amount of sludge in the converging shell 801 decreases. After the converging shell 801 is hollowed, a negative pressure suction is generated. After the converging shell 801 generates a negative pressure suction, the silt that has been lifted and dispersed in the silt gathering is absorbed by the ground pipe 7. The convergence tank 5 is cleaned;

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 ratio planting platform 3, and then decomposes the decomposed solid waste due to the effect of the self-flow of the wetland waste water. The wastes are collected in the designated area by stage-by-stage precipitation, and then the sludge that has reached the precipitation height is lifted, scattered, sucked, and recycled by setting the ultrasonic sensor 12, the spray cleaning component 6, the ground pipe 7 and the self-priming conveyor 8, so as to realize The solid waste recycling work of the wetland is ensured to continue the work, and the problem of high sludge sedimentation caused by traditional wetlands after long-term operation is solved, which is inconvenient to clean up and easily causes environmental pollution.

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)

1.一种整体式人工湿地废水处理系统,其特征在于,包括:1. an integral constructed wetland wastewater treatment system, is characterized in that, comprises: 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. 2.根据权利要求1所述的一种整体式人工湿地废水处理系统,其特征在于,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。2 . The integrated constructed wetland wastewater treatment system according to claim 1 , wherein the environmental information of wetland wastewater purification is determined by the external average temperature within the wetland wastewater area, the internal average temperature within the wetland wastewater area, the wetland wastewater The total area of plants in the wastewater area, the average density of plants per unit in 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 wetland sludge deposition information is that the wetland sludge deposition unit time is high, and the wetland The transparency of wastewater and the influent volume of wetland wastewater. 3.根据权利要求2所述的一种整体式人工湿地废水处理系统,其特征在于,基础分析模型的具体工作步骤如下:3. a kind of integral constructed wetland wastewater treatment system according to claim 2, is characterized in that, the concrete working steps of 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
Figure FDA0003618652330000021
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
Figure FDA0003618652330000021
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.
4.根据权利要求3所述的一种整体式人工湿地废水处理系统,其特征在于,湿地深度评测单元的具体工作步骤如下:4. a kind of integral constructed wetland wastewater treatment system according to claim 3, is characterized in that, the concrete working steps of 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. 5.根据权利要求4所述的一种整体式人工湿地废水处理系统,其特征在于,文本编辑单元的具体工作步骤如下:5. a kind of integral constructed wetland wastewater treatment system according to claim 4, is characterized in that, the concrete working steps of 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. 6.根据权利要求1所述的一种整体式人工湿地废水处理系统,其特征在于,湿地废水处理单元包括湿地废水处理单元包括湿地底基(1),所述湿地底基(1)对称设置,所述湿地底基(1)的顶端安装有湿地围框(2),所述湿地底基(1)设有等比种植台(3)和等比隔板(4),所述等比隔板(4)和等比隔板(4)之间间隙配合构成淤泥汇聚槽(5),所述等比种植台(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,所述等比种植台(3)和等比隔板(4)的高度均等量依次变小,所述淤泥汇聚槽(5)适配有喷洒清洁组件(6),所述淤泥汇聚槽(5)的底端贯通连接有地管(7),所述地管(7)的另一端贯通连接有自吸输送器(8),所述自吸输送器(8)上安装有控制阀(14),所述湿地围框(2)贯通连接有废水进口(9),所述废水进口(9)安装有节流阀(10),所述湿地围框(2)固定等距安装有若干个分叉支柱(11),所述分叉支柱(11)上安装有超声波传感器(12)和温度传感器(13)。6. An integrated constructed wetland wastewater treatment system according to claim 1, wherein the wetland wastewater treatment unit comprises a wetland wastewater treatment unit comprising a wetland base (1), and the wetland base (1) is symmetrically arranged , a wetland enclosure (2) is installed on the top of the wetland base (1), and the wetland base (1) is provided with an equal-proportion planting platform (3) and an equal-proportion partition (4). A sludge gathering tank (5) is formed by clearance fit between the partition plate (4) and the equal-ratio partition plate (4), and the equal-ratio planting table (3) and the equal-ratio partition plate (4) are provided with a plurality of, and equal There is a one-to-one correspondence between the proportional planting table (3) and the proportional partition plate (4), the heights of the proportional planting table (3) and the proportional partition plate (4) become smaller in turn, and the silt gathering tank (5) A spray cleaning assembly (6) is fitted, the bottom end of the sludge gathering tank (5) is connected with a ground pipe (7), and the other end of the ground pipe (7) is connected with a self-priming conveyor. (8), a control valve (14) is installed on the self-priming conveyor (8), a waste water inlet (9) is connected through the wetland enclosure (2), and a throttling is installed on the waste water inlet (9) A valve (10), a plurality of bifurcated struts (11) are fixed and equidistantly installed on the wetland enclosure (2), and an ultrasonic sensor (12) and a temperature sensor (13) are mounted on the bifurcated struts (11). 7.根据权利要求6所述的一种整体式人工湿地废水处理系统,其特征在于,所述喷洒清洁组件(6)包括支撑板(601),所述支撑板(601)固定设于两个湿地围框(2)之间,所述支撑板(601)的顶面中心处固定设有往复电机(602),所述往复电机(602)的输出轴固定连接有第一转杆(603),所述第一转杆(603)的顶部固定套设与均衡盘(604),所述均衡盘(604)的两端固定连接有L形空心杆(605),所述L形空心杆(605)的内端与支撑板(601)抵接,所述L形空心杆(605)的外端固定连接有空心斜杆(606),所述空心斜杆(606)的底端与支撑板(601)的顶端滑动抵接,所述L形空心杆(605)与空心斜杆(606)贯通连接,所述空心斜杆(606)的外端固定连接有空心连接杆(607),所述空心连接杆(607)等距设有多个,所述空心连接杆(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,所述空心连接杆(607)远离空心斜杆(606)的一端固定设有空心刮板(608),所述空心刮板(608)的两侧开设有喷孔(609),所述空心刮板(608)相邻喷孔(609)的两侧与淤泥汇聚槽(5)滑动抵接,所述空心刮板(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。7. The integrated constructed wetland wastewater treatment system according to claim 6, wherein the spray cleaning assembly (6) comprises a support plate (601), and the support plate (601) is fixedly arranged on two Between the wetland enclosures (2), a reciprocating motor (602) is fixed at the center of the top surface of the support plate (601), and a first rotating rod (603) is fixedly connected to the output shaft of the reciprocating motor (602). , the top of the first rotating rod (603) is fixedly sleeved with the equalization disk (604), and the two ends of the equalization disk (604) are fixedly connected with L-shaped hollow rods (605), and the L-shaped hollow rods ( The inner end of 605) is in contact with the support plate (601), the outer end of the L-shaped hollow rod (605) is fixedly connected with a hollow inclined rod (606), and the bottom end of the hollow inclined rod (606) is connected with the support plate. The top end of (601) is in sliding contact, the L-shaped hollow rod (605) is connected through the hollow inclined rod (606), and the outer end of the hollow inclined rod (606) is fixedly connected with a hollow connecting rod (607), so The hollow connecting rods (607) are equidistantly provided with a plurality of them, the hollow connecting rods (607) and the hollow oblique rods (606) are throughly connected, and the number of the hollow connecting rods (607) and the sludge gathering tanks (5) is equal, One end of the hollow connecting rod (607) away from the hollow inclined rod (606) is fixedly provided with a hollow scraper (608), and both sides of the hollow scraper (608) are provided with spray holes (609). The two sides of the adjacent nozzle holes (609) of the plate (608) are in sliding contact with the sludge gathering groove (5), and the bottom end of the hollow scraper (608) is in sliding contact with the bottom wall of the sludge gathering groove (5), The hollow connecting rod (607) is connected through the hollow scraper (608). 8.根据权利要求6所述的一种整体式人工湿地废水处理系统,其特征在于,所述自吸输送器(8)由汇聚壳(801)、第二转杆(802)、螺纹旋叶(803)和伺服电机(804)构成,所述第二转杆(802)转动设于汇聚壳(801)内,所述螺纹旋叶(803)固定套设于第二转杆(802)的外端,所述汇聚壳(801)与地管(7)固定连接,所述伺服电机(804)固定设于汇聚壳(801)的一端,所述第二转杆(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,所述控制阀(14)设于伺服电机(804)的相对端。8 . The integrated constructed wetland wastewater treatment system according to claim 6 , wherein the self-priming conveyor ( 8 ) is composed of a converging shell ( 801 ), a second rotating rod ( 802 ), and a threaded rotor. 9 . (803) is composed of a servo motor (804), the second rotating rod (802) is rotatably arranged in the converging shell (801), and the threaded rotating blade (803) is fixedly sleeved on the second rotating rod (802) At the outer end, the converging shell (801) is fixedly connected with the ground pipe (7), the servo motor (804) is fixedly arranged on one end of the converging shell (801), and one end of the second rotating rod (802) runs through the converging The inner wall of the casing (801) extends to the outside thereof and is fixedly connected with the output shaft of the servo motor (804), and the control valve (14) is provided at the opposite end of the servo motor (804).
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