From the access mode of six types of business data and quality control status, spatial correlation of pollution traceability, time and space alignment of multi-source data, to the linkage of pollution discharge permit and law enforcement, data stop prompt and drill acceptance, the landing judgment of the splicing screen of the environmental protection monitoring center is given.
The most expensive mistake in the splicing screen plan of the environmental protection monitoring center is not that the screen is expensive to buy, but that "the environmental protection plan is written as a replica of the flood prevention plan".The core of flood control is "whether the water level rises or not, whether to transfer", and the core of environmental protection is "where pollution comes from, how to trace the source if it exceeds the standard, and how to close the law enforcement". The screen wall layout, data access and early warning linkage logic of the two are completely different. The environmental protection monitoring center faces three hard constraints that flood control does not have:Monitoring data with quality control status(Unreviewed/reviewed/invalid), the original data displayed on the large screen may be inconsistent with the final reported data;Different refresh frequencies for multi-source data(Air quality by hour, water environment by 4 hours, pollution source online monitoring by hour or real-time), the time axis is easy to dislocation when displaying on the same screen;Pollution Traceability Needs Spatial Correlation-Pollution source emission data, monitoring station data and meteorological wind direction data must be superimposed and analyzed on GIS. Cutting off the wind direction line or pollution source connection will directly affect the traceability judgment. QunmaoLCD splicing screen China source manufacturersThe value of direct supply in environmental protection projects lies precisely in the cross-screen patchwork combination of GIS, non-standard supports and long-term spare parts-the monitoring center has a long service life, and the same type of panel will be found after five years. This article is carried out in the order of "six types of data → access mode → traceability layout → screen wall backstepping → space-time alignment → law enforcement linkage → data aging → drill acceptance". Each link gives the judgment of "under what conditions to establish and under what conditions to exclude.
1. six types of business data: first distinguish between "monitoring data" and "business picture"
The display content of the environmental monitoring center can be divided into two categories according to the nature of the data:Monitoring data(on-line monitoring of air quality, water environment, pollution sources) andBusiness screen(GIS a map, video surveillance, early warning scheduling, law enforcement information). The access mode, refresh frequency and quality control logic of the two types of data are completely different.
| Business data | Typical sources | Access mode | Quality Control/Status | Responsible party |
|---|---|---|---|---|
| Air quality monitoring | State Control Station/Provincial Control Station/City Control Station Platform | Data API docking; data hierarchy (national/provincial/municipal) and audit status need to be confirmed | Original data/post-audit data; What level is the basis for over-standard determination? | Monitoring station platform manufacturer |
| water environment monitoring | Water quality automatic monitoring station and hydrological station | Data API docking; need to confirm monitoring frequency (e. g. 4 hours/time) and abnormal value processing | Water quality category determination; whether abnormal values (such as COD sudden rise) trigger alarm | Monitoring station platform manufacturer |
| On-line monitoring of pollution sources | CEMS, sewage permit platform | Docking according to HJ 212 and other protocols; it is necessary to confirm the over-standard threshold and alarm rules. | Emission concentration, emission amount; over-standard/abnormal mark | Ecological Environment Department of Pollutant Discharge Enterprise |
| A map of GIS | Ecological Environment GIS Platform | Web page collection or GIS service docking; confirm the layer (monitoring point/pollution source/warning range) and plot ownership | Layer data aging; is plotting a GIS function or a large screen function | GIS Platform Integrator |
| Video surveillance | Video platforms of monitoring points, sewage enterprises and key areas | Platform fetching stream → decoder → wall | Video freeze/cut-off tips | Video Platform Integrator |
| early warning and law enforcement | Environmental early warning platform, law enforcement system, sewage permit system | Platform push or application screen output; need to confirm linkage rules and priorities | Warning level; law enforcement records, sewage permit information linkage | Eco-Environment Sector Platform Vendors |
Does the air quality data come from the national control station or the provincial control station? Is it the original data or the audited data? Who determines the over-standard threshold of the pollution source online monitoring and what is the linkage after the alarm? The answers to these questions determine the access mode, refresh frequency and linkage logic.The plan should specify "data level, audit status, refresh frequency, linkage rules, responsible party" item by item, instead of "access through platform" in general ". If these five columns cannot be written clearly, they will pass the buck to each other in the later joint adjustment.
2. Pollution Traceability: The Core Business of Environmental Protection Different from Flood Control
The core business process of the environmental monitoring center is not "looking at the data", but "tracing the source of pollution"-when a monitoring station exceeds the standard, the dispatcher needs to answer: where does the pollution come from? Is it the local pollution source emission or the upstream transmission? What are the wind direction and diffusion conditions? What are the surrounding pollutant companies? What is the historical law enforcement record?
| Traceability Elements | Data source | Layout Requirements | What conditions must be amplified |
|---|---|---|---|
| Location and value of over-standard monitoring station | Air quality/water environment monitoring platform | GIS main research area, mark over-standard sites | The mark of the exceeding station cannot be interrupted by the patchwork. |
| Distribution of surrounding pollution sources | Pollution source online monitoring/sewage permit platform | The same GIS layer as the monitoring station, can be superimposed | Pollution source point and emission data shall be visible on the same screen. |
| Meteorological wind direction and diffusion conditions | meteorological platform | GIS layer overlay wind direction arrow or diffusion range | When the wind direction line and diffusion range cross the screen, the key direction shall not be cut off by the patchwork seam. |
| Historical trends versus the same period | Historical data of monitoring platform | Trend control area, time axis alignment | When multi-site trend curves span screens, the timeline must be consistent. |
| Enforcement Records and Sewage Permits | Law enforcement system, sewage permit platform | Side screen or pop-up window, access as required | When tracing the source, it needs to be retrieved quickly, and it cannot be opened layer by layer. |
3. screen wall reverser: calculate the number of rows and columns from the net size of the monitoring center and the traceability line of sight.
The screen wall scale of the environmental protection monitoring center is jointly determined by the wall conditions of the monitoring center, the seat layout and the window requirements of the traceability partition.
Number of candidate rows ≈ wall usable height ÷ single screen height (rounded down) Deduct maintenance space, bottom cabinet, top reservation; then use the nearest/farthest agent's line of sight to check the readability of GIS labels and over-standard values.
Taking a 55-inch single screen (approximately 1222mm × 696 mm) as an example. A municipal environmental protection monitoring center can use a clear wall width of about 5.5 meters, a clear height of about 2.8 meters, 50cm reserved at the bottom, 30cm reserved on both sides, and 20cm reserved at the top: the available width is about 4.9 meters, 4.9 ÷ 1.222 ≈ 4.0, take4 columns; Available height is about 2.1 meters, 2.1 ÷ 0.696 ≈ 3.0, take3 lines. The candidate set consists of 4 rows and 3 columns, totaling 12 blocks. If the GIS traceability area needs to display the river basin or urban map across 2 columns × 2 rows, 12 screens can be satisfied. If the monitoring center is smaller (e.g. 4 meters wide), it may only be able to make a total of 6 3 × 2 blocks, and the "trend control area" needs to be compressed into round rounds or auxiliary screens.
County-level monitoring centers are usually smaller, 2 × 2 or 3 × 2; provincial or regional monitoring centers may be larger, requiring more than 4 × 4, and considering multi-site convergence and consultation zoning. The number of screens is not determined by "budget" or "momentum", but by the window demand of the traceability partition and the agent's line of sight.
4. GIS cross-screen and patchwork: the most sensitive technical matching for pollution traceability scenarios
A GIS map is the core of environmental traceability and the most sensitive content of patchwork. The monitoring stations, pollution source points, wind direction diffusion range and administrative boundaries on the map are all continuous lines or densely marked. Cutting off by patchwork will directly affect the traceability judgment.
| GIS Content | Patchwork sensitivity | conditions of establishment | Exclude/Caution |
|---|---|---|---|
| Connection line between over-standard station and surrounding pollution source | high | The main research and judgment area has priority of 1.8mm and below; Whether the measured connection line is cut off during cross-screen display | When the 3.5mm patchwork cross-screen shows the traceability connection, the fracture feeling is obvious. |
| Wind direction arrow and diffusion range | high | When the wind direction line and diffusion boundary cross the screen, the patchwork seam shall not fall in the key direction or boundary turning point. | 0.88mm If the installation accuracy is not enough to cause uneven patchwork, the appearance may not be as good as 1.8mm |
| Monitoring site labeling | middle | When a site is marked across the screen, the patchwork must not interrupt the site name and value. | Site dense area can adjust the layout, avoid patchwork |
| Background map (non-critical area) | low | 3.5mm can be established | No need to pay 0.88mm premium for background maps |
The splicing selection of the environmental protection monitoring center should not only look at "0.88mm or 1.8mm", but should be done.interchange inspection: Use the real GIS traceability picture to observe whether the monitoring station, pollution source point and wind direction diffusion range are cut off by the seam under the target layout; If the key content is cut off, even if the seam is 0.88mm, it is not valid, and the seam level needs to be adjusted or upgraded.The millimeter number of the patchwork seam is the nominal caliber, and the interchange inspection is the acceptance caliber.
Temporal and Spatial Alignment of 5. Multi-source Data: Technical Difficulties of Environmental Protection Different from Ordinary Monitoring
The environmental protection monitoring center has many data sources and different refresh frequencies, and "time dislocation" is most likely to occur when displaying on the same screen: air quality data is 1 hour ago, water environment data is 4 hours ago, pollution source online monitoring is real-time, and video is real-time. If the dispatcher does not pay attention to the timestamp, he may judge the data of different periods as the state at the same time.
| Data source | Typical Refresh Frequency | Time limit information to be displayed on large screen | What conditions must prompt |
|---|---|---|---|
| Air quality monitoring | By hour (national control station standard) | Data timestamp (e. g. 10:00 Data) | No updates for more than 2 refresh cycles, "Data may be out of date" |
| water environment monitoring | By 4 hours or by hour | Monitoring time and water quality category | No updates for more than 2 refresh cycles, "Data may be out of date" |
| On-line monitoring of pollution sources | Hourly or real-time | Emission concentration, mark of exceedance, data time | Stop or abnormal value, display "data abnormal/stop more" |
| Video surveillance | Real-time | Picture timestamp or "real-time" identification | Freeze for more than 3-5 seconds, "signal abnormal" |
| Meteorological wind direction | Hourly or real-time | Wind direction, wind speed, data time | If the time deviation from the monitoring data exceeds 1 hour, prompt is required. |
The pollution source point on the GIS, the air quality data next to it, and the trend curve below may show the status at different times if they come from data sources with different refresh frequencies. If the dispatcher takes them as data at the same time to make a traceability judgment, the conclusion may be completely wrong.In the plan, it should be confirmed whether each data window displays a timestamp, whether the time deviation of different data sources is visible, and whether there is a "possible expiration" prompt for stop data. The platform or data access terminal is responsible for the detection of these prompts, and the large screen acceptance verifies whether the prompts are correctly presented.
6. emission permits and law enforcement linkage: a closed-loop unique to environmental protection
The early warning of the environmental protection monitoring center is not "the end of the window", but to form a closed loop of "over-standard alarm → obtaining pollution discharge permit → checking historical law enforcement → linking surrounding videos → notifying law enforcement. This closed loop determines the design of the early warning linkage module.
| Linkage steps | What needs to be displayed | Display position | Responsible party |
|---|---|---|---|
| Exceeded Alert Trigger | Name of enterprise exceeding the standard, type of pollutant, multiple exceeding the standard and time | The warning area pops up and displays prominently. | Pollution source platform |
| Transfer of sewage permit | The enterprise pollution permit information, permitted emissions, permit type | Side screen or pop-up window | Sewage permit platform |
| View historical law enforcement | Historical law enforcement records and penalties of the enterprise | Side screen or pop-up window | law enforcement system |
| Linkage peripheral video | Video of enterprise discharge outlet, factory boundary and surrounding sensitive points | Video area, multi-screen | Video platform |
| Notify law enforcement | Generate law enforcement tasks and push them to law enforcement personnel | Dispatching area | law enforcement system |
In this closed loop, the role of the big screen is "presentation and auxiliary scheduling", not "law enforcement system itself". Pollution discharge permit information, law enforcement records and law enforcement task generation are all functions of the business system. The large screen is responsible for quickly bringing up this information when it exceeds the standard and comparing it with the screen.The plan should specify "which information is provided by which system, what the large screen is responsible for presenting, and who configures the linkage rules"To avoid integrators being asked to promise that "large screens can automatically enforce the law".
7. data aging and stop more tips: environmental monitoring of the "false real-time" risk.
The "false real-time" risk of environmental monitoring data is more hidden than flood prevention: the air quality data itself is updated by the hour. If the large screen does not display the time stamp, the dispatcher may think that he is seeing the air quality at "this moment"; If the online monitoring of pollution sources stops, the over-standard alarm may be delayed or omitted.
One is the timestamp is visibleEach data window should display data time, not just numeric values.The second is to stop more tips: When the data has not been updated beyond the agreed refresh period, the window should display "Data may expire" or "Last update time: XX:XX".Three is the audit status: The air quality data has the status of "unaudited/audited/invalid". The large screen should clearly display which level of data to avoid formal research and judgment with unaudited data. These three verification points shall be written into the acceptance outline and measured by means of simulation stop.
8. budget trade-offs and source manufacturer value
The budget of environmental protection projects is usually limited, and the order of choice is recommended:First, the seam and readability of GIS traceability area are guaranteed (the core of traceability is map overlay), then the timestamp and stop prompt of multi-source data are guaranteed, then the video and law enforcement linkage are guaranteed, and finally the conference and auxiliary screen configuration are guaranteed. Don't sacrifice the size of the main research area for the patchwork upgrade of the auxiliary screen-the traceability map can be seen clearly, which is more important than the appearance of the auxiliary screen.
Qunmao LCD splicing screen China source manufacturersThe value of direct supply is reflected in three specific links in environmental protection projects. First,GIS Traceability Cross-screen Patchwork and Size Combination: The main research and judgment area needs map cross-screen display. The stitching grade and single-screen size should be customized according to the net size of the monitoring center and the traceability line of sight. The source manufacturer can combine according to the project requirements in the 43-75 inch, 8mm to 0mm gears, instead of in the standard products. Second,Non-standard bracket and installation adaptation: The wall conditions, cabinet depth and maintenance space of the monitoring center are different. The floor cabinet, front maintenance bracket or non-standard reinforcement scheme need to be customized according to the site. Third,Long-term spare parts guarantee: The service life of the splicing wall of the monitoring center is long. When replacing the unit after five years, the same type of panel or module is required. The supply of spare parts from the source manufacturer is more reliable than that of traders. Taking Qtenboard as an example, publicly available information indicates that it operates its own manufacturing facilities and supports OEM/ODM/CKD/SKD collaboration models. Its panels undergo 48-hour burn-in testing and color calibration, and its products are designed for 24/7 surveillance applications. For integrators and eco-environmental project parties, this means thatNo need to configure in the "standard screen standard bracket", but according to the actual traceability layout of the monitoring center to choose the seam, size and installation method;Spare parts supplyIt is also more controllable than that of traders. The assessment should verify the factory qualification, panel source and actual case, rather than just look at the "factory direct supply" four words.
9. drill acceptance: complete the whole system with one pollution traceability process
The acceptance of the environmental protection monitoring center cannot only test "power on and light up, and the signal can go up the wall". Should be designed once.Pollution Traceability Exercise, run the complete process of "over-standard alarm → GIS positioning → pollution source verification → weather control → law enforcement review → consultation and dispatch → recovery.
| Phase | Exercise Action | Key points of verification |
|---|---|---|
| Exceedance Alert | Simulate the AQI or water quality of a monitoring station to exceed the standard and trigger an alarm | Alarm pops up in time; over-standard sites, pollutants and time are conspicuous |
| GIS positioning | Locate stations exceeding emission standards on a GIS map and overlay nearby pollution sources. | The map is not broken across the screen; the site and pollution source labels are readable. |
| pollution source verification | To obtain emission data and emission permit information of surrounding emission enterprises | Fast data retrieval; visible time stamp; clear mark of exceeding standard |
| Meteorological control | Superimpose wind direction and diffusion conditions to judge pollution transmission direction | The wind direction line and diffusion range are continuous across the screen; the time is aligned with the monitoring data. |
| Law enforcement access | retrieve the historical law enforcement records of the enterprise and generate law enforcement tasks | Law enforcement information can be quickly accessed; task push process is normal |
| consultation scheduling | Initiate video meetings with superiors, on-site law enforcement officers | The content of the three views is correct; the audio is clear; the sharing range is controllable |
| Data stop more | Simulate a certain type of monitoring data to stop updating | The large screen displays “Data may be outdated”; it should not be mistaken for real-time data. |
| Restore | End the exercise and restore the daily layout with one key. | Layout reverts to standard state; content of each window is correct |
10. common mistakes
- Myth 1: The environmental protection plan is written as a replica of the flood control plan. The core of flood control is water level and transfer, and the core of environmental protection is pollution traceability and law enforcement closed loop. The screen wall layout, data access and linkage logic are different, and templates cannot be set.
- Misunderstanding 2: GIS only looks at the number of millimeters of patchwork across the screen, and does not do interruption inspection. If the 0.88mm patchwork seam is cut off from the traceability line or the wind direction arrow, the impact may be greater than 3.5mm and fall in the blank area. Acceptance should be measured whether the key content is cut off.
- Misunderstanding 3: "Access through the platform" as an access scheme. The data level, audit status, refresh frequency, linkage rules and responsible parties must be specified item by item, otherwise they will pass the buck to each other during joint adjustment.
- Misconception 4: Ignoring temporal misalignment among multiple data sources. Air quality by hour, water environment by 4 hours, pollution sources in real time, the same screen is not equal to synchronization. Each data window should display a time stamp, and there should be a prompt when stopping.
- Myth five: the "big screen" as a "law enforcement system". The large screen is responsible for presenting and assisting scheduling. Emission permit information, law enforcement records and task generation belong to the business system. The boundary should be clearly written to prevent integrators from being asked to promise that "large screens can automatically enforce the law".
- Misunderstanding six: spare parts are not reserved. The service life of the splicing wall of the monitoring center is long, and the same model panel is required for the replacement unit after five years. The source manufacturer's spare parts guarantee is more reliable than the trader.
XI. FAQ
environmental monitoring center splicing screen general several pieces?
There is no standard answer. First draw the draft window of the pollution traceability zone (GIS main research area, trend control area, video area, early warning law enforcement area, conference area), then use the net size of the monitoring center to reverse the number of candidate columns and rows, and use the nearest/farthest seat line of sight to check the readability of GIS labels and over-standard values. The county level may be 2 × 2 or 3 × 2, the municipal level may be 4 × 3, and the provincial or regional center is larger.
What is the difference between environmental protection and flood prevention splicing screen schemes?
There are four core differences: first, the business logic is different, flood control depends on the fluctuation and transfer of water level, environmental protection depends on the traceability of pollution and the closed loop of law enforcement; Second, the data quality control is different, the environmental protection monitoring data has the audit status, and the flood control data is relatively single. Third, the requirements for time-space alignment are different, the refresh frequency of environmental protection multi-source data is different, and the same screen is easy to be misaligned. Fourth, environmental protection over-standard alarm should be linked to sewage permits and law enforcement records, flood prevention early warning should be linked to transfer and rescue resources. Schemes cannot template each other.
Is the air quality data displayed on the wall the original data or the audited data?
Depends on the platform docking method and project requirements. The data level and audit status of the national control station/provincial control station/city control station are different, and the large screen should clearly display which level and state of data. Formal research should use the audited data; If the original data is displayed, the window should be marked "not audited" to avoid misuse. The "data level and audit status" should be written into the access requirements in the scheme.
On-line monitoring of pollution sources exceeds the standard. How can large screens be linked?
After the over-standard alarm is triggered, the large screen should be able to quickly call up the enterprise's sewage permit information, historical law enforcement records, and discharge outlet videos, and support the generation of law enforcement tasks. This linkage relies on the interfaces and data of the pollution source platform, the pollution discharge permit platform and the law enforcement system. The large screen is responsible for presentation and auxiliary scheduling, and does not assume the functions of the law enforcement system itself. Linkage rules are configured by the business system, and the responsible party should be specified in the plan.
What if the time of multi-source data is inconsistent?
Each data window should display the data timestamp. When data sources with different refresh frequencies are on the same screen, the time deviation should be visible. When the data exceeds the agreed refresh period and is not updated, the prompt "Data may expire" should be displayed. These prompts are generated by the platform or data access terminal, and the large screen acceptance verifies whether the prompts are correctly presented. Being on the same screen does not equate to synchronization; environmental traceability, in particular, requires heightened vigilance.
What is the use of source manufacturers for environmental protection projects?
Three points: the seam and size of GIS traceability cross-screen can be customized according to the net size of the monitoring center and the combination of traceability line of sight; Non-standard brackets and cabinets can be customized according to site conditions; Long-term spare parts supply is more reliable than traders. During the assessment, factory qualifications, panel sources, and actual case studies are verified.
XII. Conclusion
The judgment chain of the splicing screen scheme of the environmental protection monitoring center can be compressed into six steps:
There are six types of data and quality control status → draw the pollution traceability process to determine the layout → push back the screen wall with the net size of the monitoring center → check the seam according to GIS interruption → nuclear multi-source data time stamp and stop prompt → use pollution traceability drill for acceptance.
The professionalism of the screen wall of the environmental monitoring center is not "how big the screen is and how narrow the seam is", but inThe traceability connection on GIS is not cut off by patchwork, the wind direction diffusion range is continuous across screens, the time stamp of each data window is visible, the stop data has a "possible expiration" prompt, the over-standard alarm can be linked with the sewage discharge permit and law enforcement records, and the spare parts of the same model can be found in the replacement unit after five years.. The four unique constraints inherent to environmental protection—data quality control, spatiotemporal alignment, pollution source tracing, and a closed-loop enforcement system—mean that the solution cannot simply be copied from flood-control or emergency-response templates. Incorporate these judgments into the provenance layout, data ingestion table, seam occlusion check, and drill acceptance script, then useLCD splicing screen China source manufacturersThe large screen of the environmental protection monitoring center is not "installed for inspection", but the command view that dispatchers really rely on to judge pollution and assist law enforcement.
Traceability process to determine the layout, GIS cut off to determine the seam; Data time should be visible, stop more prompt can not be less.
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Published: 2026-10-23
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