Disclosure of Invention
The invention aims to provide an intelligent detection treatment system for water pollution, which combines agricultural information with the system, establishes a canal pollution water treatment system according to ammonia nitrogen concentration lifting factors, enables canal water bodies to be monitored and removed under a long-flow pollution state, and solves the problems in the background technology by using sewage treatment frequency.
In order to achieve the above purpose, the present invention provides the following technical solutions:
The intelligent detection processing system for the water pollution comprises a monitoring cloud end, a plurality of water ammonia nitrogen detectors which are arranged at equal intervals along an open channel from a water inlet end to a water outlet end, a planting area module which is arranged in a farmland of an open channel irrigation coverage area, an acquisition starting control module which controls the opening of the water ammonia nitrogen detectors, and a turbulence processing module which is arranged at the tail end of the water channel;
The acquisition starting control module comprises a fixed high-frequency starting unit for controlling the water ammonia nitrogen detector to be intermittently started in the interval of 4 months to 5 months and 9 months to 10 months and a fixed low-frequency starting unit for controlling the water ammonia nitrogen detector to be intermittently started in the interval of 6 months to 9 months;
The planting area module comprises a fertilization recording unit and a climate recording unit, and the passive starting unit controls the starting of the water ammonia nitrogen detector according to the recording time of the fertilization recording unit, the climate recording unit or the recording period of the fertilization recording unit after fertilization, the climate recording unit records the rain stage and the rain stop stage;
the planting area module monitors ammonia nitrogen acquisition data of the water ammonia nitrogen detector, and sends the ammonia nitrogen acquisition data to the turbulence processing module after the ammonia nitrogen acquisition data exceeds a specified standard;
The turbulence processing module processes data through the data processor, the data processor calculates liquid inlet flow according to the liquid inlet flow unit, water flows through the turbulence unit to form a plurality of turbulence areas, the ammonia nitrogen collecting data are combined to control the throwing speed of the quantitative throwing device, and ammonia nitrogen treating agent is thrown into the turbulence areas.
As a still further proposal of the invention, the turbulence treatment module also comprises a liquid inlet flow rate unit, the liquid inlet flow rate unit calculates the port flow rate of the liquid entering the turbulence unit, when the total length of the turbulence unit and the port flow rate ratio of the turbulence unit are smaller than 5-6min, a reservoir arranged at the tail end of the turbulence treatment module is opened, so that liquid is temporarily stored in the reservoir and the liquid level of the reservoir is raised, and the liquid is discharged to the outside through a high-level discharge pipeline of the reservoir.
As a still further scheme of the invention, the water ammonia nitrogen detector is arranged at the bottom of the open channel slab bridge, the water ammonia nitrogen detector is arranged at the bottom surface of the bridge body and above the liquid level, and the water ammonia nitrogen detector is provided with a telescopic water taking structure.
In still a further scheme of the invention, the fixed low-frequency starting unit is used for controlling the starting frequency of the water ammonia nitrogen detector until the water parameters acquired by the water ammonia nitrogen detector are qualified, and the fixed low-frequency starting unit is used for controlling the starting frequency of the water ammonia nitrogen detector after the passive starting unit is triggered and started.
According to the water ammonia nitrogen detector, the quantitative dispenser is arranged, the planting area module closes a water inlet gate of an open channel (100) and an inlet gate of a turbulence processing module according to a fertilization period recorded by the fertilization recording unit, and controls the passive starting unit to start after a fertilization procedure recorded by the fertilization recording unit is finished, so that the collection starting control module controls the water ammonia nitrogen detector to start and detect, controls the quantitative dispenser at the water ammonia nitrogen detector to start and put according to ammonia nitrogen data, and starts the gate to finish flow production after putting is finished.
Compared with the prior art, the invention has the beneficial effects that:
According to the invention, the planting area module is combined with the acquisition starting control module, so that the sewage state monitoring period is matched with the pollution period, the sewage treatment accuracy is improved, meanwhile, the energy consumption is saved, the turbulence area is arranged at the tail end by utilizing the running water characteristics of the canal, the remover is put in the turbulence point position, the flow time of the water body is monitored by utilizing the flow velocity, and the ammonia nitrogen concentration of the sewage entering other water bodies or underground pipe networks can meet the discharge standard in a temporary or direct discharge mode through the reservoir according to the flow velocity.
Detailed Description
Referring to fig. 1-4, in this embodiment, the system includes a monitoring cloud 4, a plurality of ammonia nitrogen detectors 3 in water body and arranged at equal intervals along an open channel 100 from a water inlet end to a water outlet end, a planting area module 1 arranged in a farmland of an irrigation coverage area of the open channel 100, an acquisition start control module 2 for controlling the opening of the ammonia nitrogen detectors 3 in water body, and a turbulence processing module 5 arranged at the tail end of the water channel.
In the embodiment, the monitoring cloud 4 is a monitoring total station, and the water ammonia nitrogen detector 3 is provided with a data transmission module for transmitting ammonia nitrogen content detection parameters of the water to the inside of the monitoring cloud 4, and the monitoring cloud 4 is used for monitoring the whole open channel 100. The planting area module 1 has two forms and exists, the first type is the monitor terminal that intelligent agriculture used, and the inside has soil monitoring module and data analysis module, judges through data analysis whether need fertilize to control unmanned aerial vehicle or issue fertilization instruction when needs fertilize, planting area module 1 can monitor the weather simultaneously, records the rainfall problem of weather. The climate recording unit 2 is mainly used for controlling the starting of the water ammonia nitrogen detector 3, and energy can be saved by controlling the starting and the stopping of the water ammonia nitrogen detector 3 through the climate recording unit 2 due to long irrigation period. And the turbulence treatment module 5 is used for treating the flowing water in the irrigation canal under the abnormal state detected by the water ammonia nitrogen detector 3, so that the problem of water pollution diffusion caused by the polluted water entering the underground water or the pipe network is avoided.
In the embodiment, the acquisition starting control module 2 comprises a fixed high-frequency starting unit 21 for controlling the intermittent starting of the water ammonia nitrogen detector 3in the interval of 4 months to 5 months and 9 months to 10 months, and a fixed low-frequency starting unit 22 for controlling the intermittent starting of the water ammonia nitrogen detector 3in the interval of 6 months to 9 months, and the planting area module 1 comprises a fertilization recording unit 11 and a climate recording unit 12, wherein the passive starting unit 23 controls the starting of the water ammonia nitrogen detector 3 according to the recording time of the fertilization recording unit 11 and the climate recording unit 12 or after the fertilization recording unit 11 records fertilization, the climate recording unit 12 records a rain stage and a rain stop stage.
In the embodiment, most plants are fertilized in spring for 4 months to 5 months and fertilized in autumn for 9 months to 10 months, and the total fertilized amount of the two fertilized periods in spring and autumn accounts for 60% -80% of the total fertilized amount of the whole crops, so that the fixed high-frequency starting unit 21 is controlled by the time recording module, is started in the spring fertilized period and the autumn fertilized period, and adopts a high-frequency acquisition mode to acquire the high frequencies in the two time periods, wherein the frequency is less than 24 hours, and the irrigation period in summer is6 months to 9 months, and in the period, the additional fertilizer amount is small, so that the low-frequency acquisition is adopted, and the acquisition frequency is in a unit of day. Because the open channel 100 crosses the whole planting area, in the irrigation process, fertilizer often falls from the top, fertilizer is very easy to get into the aquatic through the open channel 100 from the top, simultaneously after the fertilization, the ammonia nitrogen concentration of soil also can promote, receive the influence of osmotic effect, also easily pollute surrounding water area, and the ammonia nitrogen concentration in the soil promotes the back and also can receive the transmission influence of rainwater after the rainfall and lead to the ammonia nitrogen concentration in the ditch to improve, therefore set up passive start unit 23, passive start unit 23 can control the water ammonia nitrogen detector 3 to start according to fertilization record unit 11, climate record unit 12's appearance condition, or control fixed high frequency start unit 21 or fixed low frequency start unit 22 start, thereby make control high frequency period and pollution period correspond.
In the embodiment, the planting area module 1 monitors ammonia nitrogen acquisition data of the ammonia nitrogen detector 3 of the water body, and after the ammonia nitrogen acquisition data exceeds a specified standard, the ammonia nitrogen acquisition data are sent to the turbulence processing module 5, the turbulence processing module 5 processes the data through the data processor 51, the data processor 51 calculates the liquid inlet flow according to the liquid inlet flow unit 52, the water flow passes through the turbulence unit 55 to form a plurality of turbulence areas, the ammonia nitrogen acquisition data are combined to control the throwing speed of the quantitative throwing device 54, and the ammonia nitrogen treating agent is thrown into the turbulence areas.
In the embodiment, the irrigation canal is flowing water, so that the problem of the water body needs to be solved under the flowing condition after the water body is polluted by ammonia nitrogen. At present, the ammonia nitrogen remover for the water body is a mode which is most suitable for the use of irrigation channels, and only needs to be put into the water body for full mixing. But in long-distance flow conditions, how to mix well is a problem. Therefore, the turbulence processing module 5 is disposed at the end of the canal, firstly, the data processor 51 needs to collect ammonia nitrogen parameters collected by the ammonia nitrogen detector 3 of the water body closest to itself or installed at the water inlet of the turbulence processing module 5, and records the inlet flow of the turbulence processing module 5 through the inlet flow unit 52, and the quantitative dispenser 54 is controlled to perform orderly dispensing according to the flow, referring to fig. 4, when the liquid passes through the turbulence unit 55, the middle flow channel is influenced by the reverse acting force of the two side flow channels to form turbulence in the staggered area, the turbulence processing module 5 is located above the turbulence position, the turbulent flow complex fluid direction promotes the remover to be fully mixed with the water body and flow backward, the number of the turbulence units 55 can be set to be multiple, the flow speed of the liquid in the turbulence area can be reduced, the time of the water body passing through the turbulence unit 55 can be controlled to be 5-6min by increasing the number of the turbulence units 55, and the remover is completely reacted, the liquid ammonia nitrogen concentration is discharged after being reduced, so as not to pollute the environment.
In this embodiment, the turbulence treatment module 5 further includes a liquid inlet flow rate unit 53, the liquid inlet flow rate unit 53 calculates a port flow rate entering the turbulence unit 55, and when a total length of the turbulence unit 55 and the port flow rate ratio of the turbulence unit 55 are less than 5-6min, the reservoir 6 disposed at the end of the turbulence treatment module 5 is opened, so that the liquid is temporarily stored in the reservoir 6 and the liquid level of the reservoir 6is raised, and the liquid is discharged to the outside through a high-level discharge pipe of the reservoir 6.
In this embodiment, the inflow unit 53 may be disposed at a plurality of turbulence units 55, or disposed at an inlet end and an outlet end of the turbulence units 55, and the residual duration of the running water in the turbulence units 55 is obtained by combining the flow speed difference and the length, and when the flow speed of the inflow unit 53 is too high, the reaction of the removing agent is incomplete, and for the precipitating removing agent, the precipitate is also put into other water bodies or pipe networks. Therefore, the water reservoir 6 is arranged, on one hand, substances can be precipitated in the water reservoir 6, on the other hand, the water reservoir can play a role in buffering, and when water flow is large in a rainfall state, the water reservoir plays a role in emergency treatment.
In the embodiment, the water ammonia nitrogen detector 3 is arranged at the bottom of the slab bridge 200, the water ammonia nitrogen detector 3 is arranged at the bottom surface of the bridge body and above the liquid level, and the water ammonia nitrogen detector 3 is provided with a telescopic water taking structure.
In the embodiment, in order to avoid bacteria breeding caused by long-time distribution of the water taking structure in the water body, the water taking mechanism is normally positioned above the liquid level, and the water taking mechanism of the water body ammonia nitrogen detector 3 is controlled to penetrate into the water body to take water when needed. The slab bridge 200 is provided with a plurality of equidistant slab bridges 200 for the convenience of passing in order to meet the passing of people, so that the slab bridge 200 can be just used as the installation area of the ammonia nitrogen detector 3 in the water body.
In the embodiment, the fixed low-frequency starting unit 22 controls the starting frequency of the water ammonia nitrogen detector 3 until the water parameters acquired by the water ammonia nitrogen detector 3 are qualified, and the fixed low-frequency starting unit 22 is switched to control after the passive starting unit 23 triggers the starting, and the fixed low-frequency starting unit 22 is closed, and the fixed high-frequency starting unit 21 controls the starting frequency of the water ammonia nitrogen detector 3 until the water parameters acquired by the water ammonia nitrogen detector 3 are qualified.
In this embodiment, when the fixed low-frequency starting unit 22 controls the ammonia nitrogen detector 3 in the water body at a low-frequency stage, the ammonia nitrogen concentration of the water body is not out of standard, and because the fixed low-frequency starting unit 22 also performs fertilization during the control period, but the fertilizing amount is small, when the passive starting unit 23 controls the ammonia nitrogen detector 3 in the water body to be opened after fertilization, the ammonia nitrogen concentration in the water body is detected to be higher than the set concentration, the subsequent sewage treatment process is triggered, but the risk still exists, and therefore the fixed high-frequency starting unit 21 is adopted to control the ammonia nitrogen detector 3 in the water body to be opened at a high frequency for monitoring the water body until the ammonia nitrogen concentration in the water body is reduced.
In the embodiment, a quantitative dispenser 54 is arranged at the position of the water ammonia nitrogen detector 3, under the fertilization period recorded by the fertilization recording unit 11, the planting area module 1 closes a water inlet gate of the open channel 100 and an inlet gate of the turbulence processing module 5, and controls the passive starting unit 23 to start after the fertilization procedure recorded by the fertilization recording unit 11 is finished, so that the collection starting control module 2 controls the water ammonia nitrogen detector 3 to start and detect, controls the quantitative dispenser 54 at the position of the water ammonia nitrogen detector 3 to start and put according to ammonia nitrogen data, and opens the gate to finish flow production after the putting is finished.
In this embodiment, the canal is often used in a large-area planting area, multiple types of crops are arranged in multiple areas, different crop areas are different and have different habits, so that in order to avoid the problem that the water body in the local area pollutes a certain section of the canal and is not treated until the water body reaches the tail end, the quantitative dispenser 54 is also synchronously arranged at the ammonia nitrogen detector 3 of the water body, and in the monitoring stage, after the quality of the water body in a certain section is in a problem, the quantitative dispenser 54 in the rear section can be started for dispensing, so that the influence of the water body on the rear area is avoided.
In the embodiment, when the ammonia nitrogen detectors 3 of the open channel 100 for multiple sections of water bodies detect the problem of high-concentration ammonia nitrogen, the gate of the water inlet of the open channel 100 and the gate of the inlet of the turbulence treatment module 5 can be closed, and the water is put in by the quantitative dispenser 54 below the slab bridge 200, so that the water is kept stand for 5min for full reaction and then is discharged to the tail end.
The foregoing description is only a preferred embodiment of the present invention, but the scope of the present invention is not limited thereto, and any person skilled in the art, who is within the scope of the present invention, should make equivalent substitutions or modifications according to the technical solution of the present invention and the inventive concept thereof, and should be covered by the scope of the present invention.