— Blogs —
—Products—
Consumer hotline +8618073152920 WhatsApp:+8615367865107
Address:Room 102, District D, Houhu Industrial Park, Yuelu District, Changsha City, Hunan Province, China
Product knowledge
Time:2026-04-18 11:22:24 Popularity:675
A swimming pool monitoring retrofit should be accepted as an installed measuring loop, not just as two functioning probes. Verify the chlorine reporting quantity, sample travel time, pH measurement, receiver interpretation and chemical-feed interlocks. NiuBoL sensors can provide the measurement inputs, but the existing panel, sample plumbing and controller must be assessed before a direct replacement is approved.

Photograph and label the installed instruments, sample connections and controller terminals. Record the disinfectant, stabilizer use, pool circuit and current test method. Establish whether the old input accepts a raw electrode, a current loop or serial data. Those interfaces are not interchangeable simply because the screen labels both channels pH or chlorine.
Determine which components remain in service: sample pump, flow cell, valves, flow switch, controller and chemical-feed equipment. Include their condition in the retrofit assessment. Replacing a sensor while retaining a leaking cell or an unreliable flow switch can leave the original operating problem unresolved.
Obtain the facility's applicable operating requirements before selecting ranges or alarm settings. CDC guidance for public-pool operation includes independent testing, staff responsibilities and maintenance alongside monitoring. The site's governing requirements and operating programme still apply after an online panel is installed.

The NBL-WQ-CL measures on an HClO basis using a constant-voltage method. HClO is hypochlorous acid, not an automatic synonym for every free-chlorine result. Require agreement on the reported quantity, compensation and comparison procedure before copying the former controller's thresholds into the new channel.
Pool chemistry matters. Stabilized chlorine, salt-water chlorination and unusual pH conditions require suitability review for the proposed configuration. A successful check at one concentration does not establish performance across every condition. If the required duty exceeds the offered measuring range, select a different suitable arrangement rather than using the end of the scale as an operating target.
Review the pH channel at the same time because pH affects chlorine interpretation. The two readings must represent the same circulating water. A pH probe in one stagnant branch and a chlorine probe in another flowing branch can create a misleading paired trend even if both devices communicate normally.

Sample travel time depends on the wetted volume between take-off and sensing point divided by sample flow. Use actual internal dimensions, cell volume and measured flow. This delay is additional to sensor response and controller filtering. A fast polling interval does not remove any of these delays.
For an illustrative branch with 0.24 L of upstream wetted volume, a flow of 30 L/h is 0.5 L/min. Nominal transport time is 0.24 / 0.5 = 0.48 minutes, or 28.8 seconds. At 60 L/h it becomes 14.4 seconds. These are ideal volume/flow estimates, not measured response times or instructions to increase flow beyond the selected cell's limits.
Measure the installed behavior during commissioning. Dead spaces, mixing and partially blocked tubing can make the real response slower than the simple estimate. Document the normal sample flow and the point where an independent comparison sample is taken so later maintenance checks can reproduce the same condition.

| Item | NBL-WQ-CL | NBL-WQ-PH base model |
|---|---|---|
| Range | 0-2.000 mg/L HClO | 0-14 pH |
| Resolution and accuracy | 0.001 mg/L; +/-5% or +/-0.05 mg/L | 0.01 pH; +/-0.1 pH |
| Water temperature | 5-50 C; Pt1000 compensation | 0-65 C; NTC compensation |
| Pressure | Below 0.1 MPa | Below 0.2 MPa |
| Wetted housing materials | POM and PTFE | POM |
| Installation | Matching flow cell, 30-60 L/h; medium pH 4-9 | Immersion installation, 3/4 NPT |
| Supply and power | 12-24 VDC +/-10%; 0.2 W at 12 V | 12-24 VDC; 0.2 W at 12 V |
| Output, protection and cable | RS485 Modbus RTU; IP68; standard 5 m | RS485 Modbus RTU; IP68; standard 5 m |
For the base chlorine configuration, confirm how the percentage and absolute error terms apply near the required control point. The sensor's stated response is below 30 seconds; transport delay remains additional. These component specifications do not establish the completed panel's regulation performance.

Check the pH holder against the full assembly, not just the nominal thread. Establish immersion, clearance and service access. A reusable cabinet may still need new internal mounting or cable entries. Waterproof the connections appropriately; IP68 on the probe does not provide an ingress rating for the cabinet, external terminals or a reused power supply.
Do not transfer the base pH specifications to a PH-4 replacement. Confirm temperature compensation, wetted materials and actual output for the ordered model. For maintenance planning, pH electrode storage and chlorine electrode conditioning are separate procedures. A potassium-chloride storage instruction for glass pH electrodes must not be applied indiscriminately to the chlorine channel.

Read each sensor independently before connecting the complete bus. Assign distinct device addresses and verify the delivered serial settings. Compare the probe result with the controller's engineering value, including temperature and any valid status information. Remove obsolete receiver offsets or scaling only after identifying their purpose and recording the approved change.
Keep write access for calibration and configuration out of routine polling. If the existing panel accepts only analogue signals, specify an appropriate supported interface or replacement controller. A serial-to-current conversion is a separate engineered function, not a wiring change between A/B terminals and an analogue input.

Use the responsible engineer's approved commissioning method to test loss of sample flow, sensor disconnection, communication timeout and controller restart. Chemical-feed equipment must respond through its approved independent protections. Do not provoke a hazardous water condition or bypass circulation interlocks merely to observe a sensor alarm.
A displayed low chlorine value can mean a real residual change, loss of representative sample or an instrument problem. The controller must not treat every invalid or missing input as an instruction to increase feed. Confirm the configured response and authorized recovery procedure for each fault, including which indication reaches the operator.

Compare online and independent results from the same sample condition, with their methods and times recorded. Repeat across the intended operating conditions. Agreement achieved by changing a calibration coefficient at one point is insufficient if pH, stabilizer or flow changes later produce unacceptable differences.
Keep an acceptance record covering actual flow, measured delay, correct channel values, fault responses and restored operation. Inspect the chlorine sensing end and cell as part of the service plan. Alternative chlorine assemblies have their own installation and performance requirements; a similar metal housing does not make their cells interchangeable.

Only if the ordered probe's fit, hydraulic requirements, pressure, materials and service arrangement are confirmed. A physically possible insertion does not establish acceptable measurement conditions.
Check sample transport, sensing response, controller filtering and timestamp alignment. Calculate volume divided by flow as a starting estimate, then measure the installed delay before changing alarm logic.
No. Opening decisions follow the facility's operating and inspection requirements. Online pH and chlorine inputs do not replace all required independent tests, visual checks or trained operator decisions.
Only when the existing controller cannot provide the required data path. Specify the missing function, destination and interface. Do not add a gateway when a verified compatible local connection already meets the duty.
Provide the existing panel models and input types, sample drawing, disinfectant and stabilizer details, required reporting range, pressure, flow and acceptance procedure. Identify reusable parts so NiuBoL can assess the actual replacement scope.

A swimming pool monitoring retrofit succeeds when new measurements remain representative and usable in the retained installation. Confirm chlorine chemistry, quantify sample delay, verify receiver compatibility and test protective functions separately. Any additional transparency measurement has a different purpose and cannot substitute for chlorine, pH or the facility's required safety checks.
NBL-WQ-CL Water Quality Sensor Online Residual Chlorine Sensor.pdf
NBL-WQ-CL-4A Industrial-grade Online Residual Chlorine Sensor.pdf
NBL-WQ-CL-4S Series Online Water quality Residual Chlorine Sensor.pdf
NBL-WQ-PH Online Water Quality pH Sensor.pdf
Prev:Online pH Meter Fault Diagnosis: No Reply, Frozen Values and Slow Response
Next:Water Quality Data Analytics: Separate Measurements, Estimates and Alarms
Related recommendations
Sensors & Weather Stations Catalog
Agriculture Sensors and Weather Stations Catalog-NiuBoL.pdf
Weather Stations Catalog-NiuBoL.pdf
Agriculture Sensors Catalog-NiuBoL.pdf
Water Quality Sensor Catalog-NiuBoL.pdf
Related products
Combined air temperature and relative humidity sensor
TDR Soil Moisture & Temperature Sensor for irrigation| RS485 |4-20mA| NBL-S-THR
Soil pH sensor RS485 soil Testing instrument soil ph meter for agriculture |NBL-S-PH
Wind Speed sensor Output Modbus/RS485/Analog/0-5V/4-20mA
Tipping bucket rain gauge for weather monitoring auto rainfall sensor RS485/Outdoor/stainless steel
Pyranometer Solar Radiation Sensor 4-20mA/RS485
Screenshot, WhatsApp to identify the QR code
WhatsApp number:+8615367865107
(Click on WhatsApp to copy and add friends)