8. Managing a Monitoring Station

Last updated on 2023-06-27

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Management of the EnviroDIY Monitoring Station includes quality control practices, sensor cleaning, station maintenance, power issues, data curation, and other logistical issues associated with keeping a monitoring station functioning properly. Important considerations in overall station management are:

• For quality control, monitoring station data should be cross-checked by conducting on-site measurements with calibrated handheld probes.
• For quality control, all monitoring station data should be backed up on a secure server or hard drive.
• Sensor cleaning should be done according to what the data dictate (i.e., if data indicate fouling, sensors should be cleaned). The Campbell OBS-3+ turbidity sensor is particularly vulnerable to fouling and generally needs to be cleaned on a weekly basis.
• Battery levels below 3.6 V indicate that monitoring station function is at risk and alternative power options should be explored.
• For quality control, maintenance and sampling should be documented using the Field Visit Data Form or in waterproof field notebook. Copies of field data sheets and/or notebooks should be made on a regular basis and stored in a secure location.

8.1 Quality Control

• View the Recommended Roles/Responsibilities for Managing an EnviroDIY Monitoring Station quick guide for a complete overview of proper monitoring station management.
• Consult the EnviroDIY Monitoring Stations – Quality Control Quick Guide for detailed quality control protocols.
• See the EnviroDIY Monitoring Stations – Field Visit Data Sheet Tutorial for detailed instructions on completing the EnviroDIY Field Visit Data Form.
• View a video tutorial on performing quality control at your monitoring station site.

8.1.1 Field Visit Documentation

Any time a visit is made to a monitoring station it is recommended that sensor cleaning activities, staff gauge height, photos of site and station conditions, and any other maintenance and/or monitoring activities described in section 8.2, as well as supplemental data collection activities (e.g, discharge measurements and grab sample collection; see Supplemental Sampling, Rating Curves, Loads) be documented using the Field Visit Data Form (Table 8.1.1.1) or in a field notebook.

Back up copies should be made of data sheets or field notebooks on a regular basis.

In addition to basic quality control, documentation of all activities associated with monitoring station management will allow identification of issues and support improvements to the management process. Online entry is available for approved stations in the Delaware River Basin via the Delaware River Watershed Initiative Resources page on WikiWatershed.org.

To ensure integrity of the data, it is recommended that data sheets be printed on weather resistant paper (e.g., Amazon: “Rite in the Rain All-Weather Copier Paper, 8 ½” x 11″, 20# White, 200 Sheet Pack (No. 8511)”. It is also recommended that data sheets be completed using a graphite pencil — ink pens may not be effective when used on the weatherproof paper. A waterproof field notebook (e.g., Amazon: “Rite in the Rain All-Weather Hard Cover Notebook, 4 3/4″ x 7 ½”, Yellow Cover, Journal Pattern (No. 390)”) can be used instead of field data sheets, however, it should be noted that without a field sheet guide it can be easy to forget key pieces of information.

Table 8.1.1.1. Description of Field Visit Data Form

Datum	Explanation
Name(s)	Names of individuals conducting the work
Site ID	ID assigned if a monitoring station was deployed in association with the Delaware River Watershed Initiative
Stream Name	Name of stream
GPS (Lat/Long)	Site coordinates in Decimal Degrees
Photos (Yes/No)	General record of whether photos were taken — a repository for these photos may be developed
LoggerID	Running tally of all EnviroDIY monitoring stations that have been built and deployed. Each individual monitoring station has a specific SL number, e.g., SL###
Location	Simple description of general site location, e.g., nearby bridge crossing or confluence with another stream
Date, Time, AM/PM, EST/EDT	Date on which site visited; Time at which form was completed; AM/PM; Eastern Standard Time = fall/winter, Eastern Daylight Time = spring/summer
General Notes/Photo Descriptions	Space to record information about the specific visit to the site and/or to describe photos that were taken
SITE OBSERVATIONS
Staff Gauge Height (m), Time, AM/PM, EST/EDT	Water level on staff gauge measured in meters; Time at which measurement recorded; AM/PM; Eastern Standard Time = fall/winter, Eastern Daylight Time = spring/summer
Sensor-Reported Water Depth (mm), Time, AM/PM, EST/EDT	Depth reading from CTD sensor in millimeters; Time at which measurement recorded; AM/PM; Eastern Standard Time = fall/winter, Eastern Daylight Time = spring/summer
Precipitation	Amount of precipitation
Water Clarity	Coarse assessment of water clarity
MONITORING STATION MAINTENANCE
Sensors Submerged?	If sensors are not submerged or partially submerged it may be necessary to consider repositioning the sensors
Location of Sensors Changed?	Documentation of any re-location of sensors. If rating curves are being developed moving sensors may require assistance from Stroud Water Research Center
Cleaned Sensors? Exact time	Important to document exact time when sensors were cleaned – allows reference to specific spot in time-series data
Retrieved Memory Card?	Memory card needs to be removed to supplement online data if gaps exist or if online data are not available
Changed Batteries?	Batteries may need to be changed if solar charging is inadequate — record of this will help characterize site conditions
Cleaned Solar Panel?	Solar panel may collect dust or debris; record of this will help characterize site conditions
Other monitoring station maintenance?	Describe any other situational issues
GRAB SAMPLE INFORMATION
Grab Sample Taken?	Record of collection of sample
Sample Number	Specific number listed on grab sample bottle — unique number for every bottle — this is an important detail to record
Bottle Type	“Square Nalgene” 1 L or 500 mL
Lab Sent To	Lab that will analyze sample, usually this is the Stroud Center
Time	Exact time (to the minute) that the grab sample was collect — this is an extremely important detail to record because it will allow the grab sample data to be matched with specific sensor measurements at the time grab was collected
Volume	Grab samples will either be 500 mL or 1 L
Date Shipped	Date when sample was delivered to FedEx for shipment
Chain of Custody #	Specific number from Chain of Custody form provided in grab sample shipping kits
IN-SITU MEASUREMENTS
Field Meter Brand/Model/Serial#	Record of the instrument used to collect the data
Was meter calibrated? Standard, Calibration Result	Record of calibration
OTHER PARAMETERS (e.g., NITRATE, PHOSPHATE, CHLORIDE, pH, DO)
Parameter, Brand/Model, Result	Record of any other measurements using kits, meters, or other methods
OTHER INFORMATION
Field duplicate Taken of Grab Sample?	Sometimes grab samples may be collected in duplicate for quality control purposes
Performed Cross-Section Survey?	Cross-section survey is done when monitoring station is installed — mapping of channel profile for predicting cross-sectional wetted area for use in calculating discharge
Flow Measurement w/ Flow Meter?	Discharge measurements collected using a flow meter
Flow Measurement w/ Neutrally Buoyant Object	Discharge measurements collected using a timed float of a neutrally buoyant object
Flow Measurement w/ another method?	Discharge measurements collected using any number of methods including timed fill, salt-dilution, etc.

8.1.2 Data Backup

View a video tutorial on downloading data (i.e., backing up data) at your monitoring station site.

Although data can be stored on Mayfly logger’s microSD card and the Monitor My Watershed data portal also has long-term data storing capacity, data should be backed up to a secure hard drive or server on a regular basis. Recommended data back-up frequency is every six to eight weeks if data are transmitted to the data portal and every two weeks if data are only stored on the microSD card. This process ensures that long term data records are secure even if damage to Mayfly Data Logger, microSD card, or a website malfunction occurs.

Downloaded data files should be filed chronologically and each file title should include a unique identifier for the particular station and the date range or download date of the file.

Some monitoring stations have intermittent cell coverage which could cause data transmission to the Monitor My Watershed website to stop. When this happens, sensor data will continue to be stored on the microSD card and missing data can be retrieved from it. Any data recorded on the card during a cellular outage will not be transmitted to the website once the cellular coverage returns.

Regardless of whether a monitoring station is online, sensor data will always be stored on the microSD card; therefore, if data stop transmitting to the website due to cell coverage issues, the complete data set can still be accessed via the microSD card. To download data from the microSD card:

1. Open the logger box.
2. Turn off the Mayfly Data Logger.
3. Remove microSD card from board.
4. Insert blank microSD card (so that data can continue being recorded).
5. Turn the Mayfly Data Logger back on.
6. Insert microSD card (the one you just removed) into a standard SD card adapter.
7. Insert adapter into appropriate port on computer.
8. Save data file to secure hard drive or server with the recommended format: SL#_mm-dd-yy.
9. Delete data from microSD card for return to Mayfly Data Logger.
10. Open data in Excel and graph as needed.

8.1.3 Sensor Cross Checks and Calibration

The Meter Hydros 21 CTD and Campbell OBS-3+ (and ClariVue10) turbidity sensors are factory-calibrated and cannot be recalibrated by the end user. (See associated manuals: Hydros 21 CTD (Gen1 version or Gen2 version); Campbell OBS-3+). However, these sensors can foul, malfunction, or get damaged, therefore, quality control cross-checks are highly recommended using independently calibrated instruments. 

All quality control measurements should be recorded in the “In-situ measurements” section of the Field Visit Data Form or in a field notebook.

Any discrepancies between monitoring station data and data collected using hand held meters and other instruments should be further investigated. If monitoring station data are identified to be inaccurate, consult the sensor user manual or the manufacturer of the sensor and consider whether the observed inaccuracy is acceptable, if there is any way to fix the problem, or if sensor replacement is necessary. 

These cross checks of monitoring station sensors should be done on a quarterly basis and more frequently if accuracy of data is questionable. A certain level of error is inherent in the monitoring station sensors and in all handheld sensors. There is no defined limit specified here for what is acceptable in terms of variability in these measurements. More importantly, measurements should always be documented and evaluated in the context of the specific project intentions for data usage. Furthermore, natural ranges of parameters should be understood so that departures from these can be identified and investigated.

Cross Checks for Conductivity, Temperature, and Turbidity

For conductivity, temperature, and turbidity, independently calibrated hand-held meters (see the Commercial Sensors in the appendix) should be used to cross-check the monitoring station sensor accuracy for these parameters. See the EnviroDIY Monitoring Stations – Quality Control Quick Guide for step-by-step instructions.

Cross Checks for Water Depth

To check the accuracy of depth measurements from the CTD sensor use a metric ruler or meter stick to measure depth from the window of CTD sensor (where pressure transducer is located) to the water surface. This hand-measured depth reading should be similar to the CTD depth sensor reading – any substantial difference between the two is a red flag that the pressure transducer is damaged or malfunctioning. 

However, it should be noted that the CTD sensor is not designed for measuring absolute depth with high precision. Instead, it is designed to measure changes in depth, which is how it is being used here (i.e., for tracking changes in discharge). Therefore, the metric ruler measurement of sensor depth should be used as a guide in tracking sensor function; the specific depth it reads should be consistent and predictable in accordance with changes in water levels.

If this is found to not be the case then the sensor may not be functioning correctly and assistance should be sought via the sensor manufacturer or the EnviroDIY forums. See the EnviroDIY Monitoring Stations – Quality Control Quick Guide for step-by-step instructions.

To ensure that the CTD sensor can be re-positioned at its original depth after being removed purposefully or by natural causes (e.g., storm flows), a staff gauge and/or stream bottom rebar can be installed. An “Offset” is then calculated that represents the difference in water depth as measured by the staff gauge or stream bottom rebar (for info on staff gauge and rebar installation see section 6) and as measured by the CTD sensor. 

This offset should remain the same over time and at different water depths. Any substantial changes to this offset indicate either a problem with the CTD sensor or with the staff gauge or stream bottom rebar. 

If the pressure transducer in the CTD sensor were to malfunction, get damaged, or removed from the stream this offset can be used to ensure that when the CTD sensor is replaced or re-installed that it can be positioned at the exact same depth at which it was previously positioned. 

Consistency in depth readings (i.e., positioning the CTD sensor at a consistent depth) is critical for developing rating curves and conducting analyses of the continuous depth data.

Cross Checks on Data Trends and Patterns

To ensure reliability of monitoring station data, data trends and patterns should be regularly evaluated. Graphical displays of data and assessment of the data in the context of the specific site conditions and ecological expectations should be used as a quality control measure to ensure data reliability.

Issues and problems to look for in data-quality assessment are extensive, but there are specific common issues that can be considered when troubleshooting for problems in sensor data. See Data Patterns and Troubleshooting in the appendix for details.

If monitoring station data appear suspicious (outside of normal range for the site, erratic, etc.) cross-checks with other calibrated sensors should be done immediately. If monitoring station data appear normal, cross-checks with handheld sensors should be done quarterly as a general quality control method.

8.2 Monitoring Station Maintenance

View the EnviroDIY Monitoring Station Parts List

Please see below for detailed maintenance protocols or consult the EnviroDIY Monitoring Stations – Maintenance Quick Guide.

For detailed instructions on completing the EnviroDIY Field Visit Data Form, read the EnviroDIY Monitoring Stations – Field Visit Data Sheet Tutorial.

View a guided video tutorial explaining sensor maintenance.

To ensure data from the monitoring station are accurate and continuous it is necessary to:

• Keep sensors clean and area around sensors free of debris.
• Keep area around logger box clear of vegetation, debris, and insects.
• Keep the solar panel clean and exposed to as much sunlight as possible.
• Maintain battery level and cellular transmission of data by ensuring the battery is > 3.7 V.

See Maintenance Checklist in the appendix for monitoring station maintenance activities and timing of these activities. The key issues in maintaining a monitoring station are:

• Logger box and Mayfly Data Logger
  • Functionality of the monitoring station is suspect if battery level falls below 3.6 V.
  • Any moisture inside the logger box can cause logger board malfunction.
  • Cycling the power (turn board off, pause 5 seconds, turn board back on) is a common fix for loss of cellular transmission and other miscellaneous issues.
• Turbidity sensor
  • Turbidity sensor is particularly vulnerable to fouling: any debris, sticks, leaves on or near it, or algae that grows on it will cause false high readings and degrade data quality.
  • Data from turbidity sensor can be affected by objects in its field of vision (38 cm); this can include debris and sediment piled up around or on the sensor and algae growing on the sensor.
  • Because of the extended field of vision of the turbidity sensor, turbidity data are suspect when water level is less than 30 cm.
• CTD sensor
  • The pressure transducer that measures water depth can be damaged if ice forms on the sensor.
  • The CTD sensor is not as prone to fouling as the turbidity sensor; however excessive debris accumulation on the conductivity Wenner array (four screw heads) will cause inaccurate conductivity readings.
  • In rare cases the Meter Hydros 21 CTD sensors could have a factory production issue that affect data accuracy. Quality control checks with calibrated handheld sensors (see Monitoring Station Management) should be used when data are suspect.

8.2.1 Cleaning Sensors In-Stream

Most of the time sensors can be cleaned without removing the sensor bundle from the stream. Depending on the site and stream conditions, and depending on weather and any other environmental influences or unforeseen technical problems with the stations, sensor cleaning frequency may range from weekly to monthly.

The Meter Hyros 21 CTD sensor cleaning involves scrubbing the semi-enclosed parts of the sensor (four point Wenner array shown in Figure 8.2.1.1) with a scrub brush to remove any accumulated dirt and debris. Cleaning the CTD sensor may not be necessary on a regular basis and is dependent on whether debris accumulates inside the partially enclosed part of the sensor.

In contrast, the Campbell OBS-3+ turbidity sensor usually needs regular cleaning as it will tend to accumulate algal growth, leaves, sticks, and debris, all of which will affect data accuracy. Unlike the CTD sensor, which is not highly affected by this type of debris accumulation, the turbidity sensor is affected by any debris within its field of vision, which extends to 38 cm from the sensor window. The rate at which this accumulation occurs is variable, so maintenance schedules should be planned on a site-specific basis (see When to Clean Sensors).

To clean the sensors in-stream:

1. Clear all accumulated debris on the stream bottom away from the sensors using hands and feet or a tool if necessary.
   1. *Note: The turbidity sensor can “see” 38 cm away from the sensor window in clean water, so make sure debris near the sensor is cleared away accordingly. If anything is in the sensor’s field of vision (e.g., rocks, accumulating sediment, stream bank, woody debris) the turbidity readings will be inaccurate.
2. Remove all large pieces of material (leaves, sticks) from the sensor bundle by hand or with the long bristles of the sensor brush.
3. Use the longer bristles of the sensor brush to gently clean the side slots on the CTD sensor (Figure 8.2.1.1).
4. If there are any sticks or hard objects wedged in the slot make sure to remove them carefully so as to not damage the pressure transducer (the white disc in the CTD sensor).
5. Use the long bristles to clean the four screw heads inside the side slot (these are the points at which conductivity is measured). Use a Q-tip to clean the screws if necessary, making sure not to touch the white pressure transducer disc above.
6. Use the short stiff bristles of the sensor brush to clean the signal window on the turbidity sensor (Figure 8.2.1.1).
7. If a sensor brush is not available, using any other plastic bristle brush or your fingers is acceptable for cleaning the sensors.

8.2.2 Removing Sensors from Water

Do not remove the sensor bundle (Figure 9.2) from the stream unless cleaning cannot be done while sensors are in the stream. If removing the sensor bundle from the stream is absolutely necessary, follow these steps:

1. Record the orientation of the sensors in the stream and note the position of the PVC conduit with regard to the top of the steel mounting stake. Also note the position and orientation of the mounting pin. When you return the sensor bundle to the stream you will need to position the sensor bundle with the same orientation and at the same level to ensure consistent data.
2. If necessary, remove tent stakes and zip ties securing the sensor cables to stream bottom and tree roots. This loosens the sensor cable so the sensors can be brought to the stream bank.
3. Remove the mounting pin; it functions like a standard safety pin.
4. Slide the sensor bundle off of the steel stake.

To remount the sensor bundle (Figure 9.2) on the mounting stake:

1. Make sure orientation of sensor bundle is the same as it was before you removed the sensor bundle.
2. Slide sensor bundle (via PVC conduit) back onto the steel stake.
3. Match holes in PVC conduit up with holes in steel stake at the same vertical level as before.
4. Slide mounting pin through both sets of holes and lock mounting pin.

8.2.3 Clearing Around the Station

Similar to the sensors, the logger box, solar panel, and associated components will require regular maintenance. All debris and vegetation should be cleared from around and above the logger station.

The logger box is waterproof but it should be opened periodically to confirm that no moisture has entered and that the Mayfly Data Logger and all other internal components are intact.

Vegetation should be cut back from around the logger box and solar panel. Although the logger box is fully sealed from the external environment, vegetation can get in the way when opening the box and can possibly introduce water, insects, and debris.

Anytime the logger box is opened it is important when closing the box to ensure that there is no grass, leaves, stems, or other debris breaching the seal: this debris will allow moisture into the box and damage the electronics.

Vegetation covering the solar panel can reduce solar exposure and can cause additional debris and dust accumulation on the solar panel. Vegetation should be cut back on a regular basis from beneath and around the logger box and solar panel using any number of different tools (Figure 8.2.3.1). Clean dust and debris from solar panel with your hand or with a soft cloth.

8.2.4 When to Clean Sensors

Generally, sensors need to be cleaned on a weekly basis and sometimes more frequently during the fall or during storms when leaves and debris are abundant.

If the four-point Wenner Array (screw heads) in the CTD sensor becomes covered in silt, algae or other debris the data will be affected. This type of fouling does not usually occur quickly so the CTD sensor will usually produce accurate data for weeks (or even months in some cases) without needing to be cleaned.

The Campbell OBS-3+ turbidity sensor generally requires much more frequent cleaning than the CTD sensor. Because the turbidity sensor functions by sending light out into the water column and then detecting reflection of this light off of suspended material, any leaves, grass, sticks, or other material attached to or near the turbidity sensor will cause false high turbidity readings.

Therefore, it is important to clean the turbidity sensor as soon as any debris attaches, particularly during storm events when it is typically most important to acquire accurate turbidity data.

Unless debris detaches naturally (i.e., carried away by the current), turbidity readings will remain inaccurate and unusable until the debris is removed. During high water conditions it may be necessary to attach a brush to a long pole in order to reach the turbidity sensor and free any attached debris (see Figure 8.2.1.1).

For developing the TSS/turbidity rating curve (see Supplemental Sampling, Rating Curves, Loads) for a site it may be necessary to clean the turbidity sensor on an hourly basis during storms. The sensor can foul more frequently than normal during storms, but this is also the time when accurate turbidity data are most important. Therefore, when attempting to develop the TSS/turbidity rating curve it may be most effective to clean the sensor hourly and collect grab samples over this same time period.

If sensor data are online, these real-time data can be used to inform timing of sensor cleaning. Normal turbidity readings for cloudy and muddy water (in the eastern U.S.) are generally < 300 NTU (although this can vary); therefore, if online turbidity readings show NTU levels well above this (e.g., > 1000 NTU) this is a strong indication that the sensor is fouled or buried. Furthermore, if turbidity readings suddenly spike and/or increase dramatically and are not associated with changes in depth (i.e., increased stream flow due to precipitation) this is also a reliable indication that fouling has occurred (see Sensor Fouling Data Patterns in the appendix).

False-high turbidity readings will also occur with algae growth on the sensor. In these cases turbidity data may increase gradually over multiple days and may be in the normal range for water conditions (i.e., <400 NTU; see Sensor Fouling Data Patterns in the appendix). Understanding the natural turbidity ranges and stream response to precipitation will help in determining when turbidity readings are suspect.

In all cases of false-high turbidity readings removal of debris and cleaning of the sensor with the sensor brush should be done as soon as possible.

8.2.5 Freezing Risk

The issue of highest concern during winter is damage to the pressure transducer in the Hydros 21 CTD sensor. The pressure transducer, as the name implies, is sensitive to pressure changes, so when water expands during freezing the pressure of the ice directly against the pressure transducer can damage it. If freezing does occur around the CTD and turbidity sensors all data will be inaccurate during this period time and should not be used.

Turbidity data should return to normal after the ice melts. Depth data will be suspect and should be closely checked after the ice melts to determine if the sensor was damaged. Temperature and conductivity data should return to normal but should also be checked to ensure accuracy after the ice thaws, as these can be affected if the pressure transducer is damaged.

The shallower the water in which sensors are positioned, the higher the risk of freezing. Monitoring air and water temperatures during the winter can be important, especially in cases where sensors are located within the part of the water column where freezing may occur. Freezing risk is generally highest in small streams where there are not deep locations available for sensor placement, but freezing may also be a risk for deeper sensors during severe and extended low air temperatures when ice layers get thicker than normal.

Ice that forms at a depth above the sensors is not a high risk to sensor integrity, but this can make it difficult to access sensors. If the ice has to be broken with a hammer or chisel there is risk of damage via direct contact of the hammer/chisel with the sensors and/or sensor cables. There is also a risk of damage to sensors through shifting pieces of ice as they are broken and through possible damage from the shock of the hammer or chisel.

If freezing of the water surface is an issue and cleaning sensors during this time period is important it is recommended that ice layers be removed on a frequent enough basis so as to not require a hammer or chisel for breaking the ice (i.e., remove ice when it can be broken by hand). Clearing ice at this frequency will ensure that the sensors are accessible for cleaning and ensuring accurate data.

8.2.6 Power Management

The target voltage level for the battery is 3.7 V or higher. Below 3.55v the station may lose functionality and data will stop transmitting to the web data portals. The typical battery voltage pattern is for the battery to charge during the day and slowly lose a little power during the night.

In certain scenarios where sunlight is restricted or diminished due to canopy coverage, cloudy days, or seasonality, battery level may decline over multiple days due to inadequate solar exposure and incomplete charging (see Data Patterns in the appendix). This gradual decline may also happen when cell coverage is intermittent, in which case the Mayfly Data Logger may make repeated and long unsuccessful attempts to send data to the website using extra power each time (see Data Patterns in the appendix).

In some cases, solar charging may vary throughout the year with seasonal canopy cover changes as well as other canopy cover changes (e.g., fallen trees, growth of vegetation). Reposition the solar panel direction to receive better sun exposure depending on the time of year.

Basic rule of thumb to follow when monitoring your online battery voltage:

• 4.0V-4.2V: fully charged battery.
• 3.7V-3.9V: sufficiently charged battery.
• 3.7V is the nominal voltage (Nominal voltage is the default, resting voltage of a battery pack). The middle ground between fully charged and the low voltage cutoff.
• 3.55V-3.7V: start to keep an eye on the battery pattern.
• 3.5V or below: if it stays at or below 3.5V for an extended period of time you may want to replace your battery. If you see that your station has dropped offline and your battery is below 3.5V, your battery died and needs to be charged or replaced.

See Battery Level as a Diagnostic in the appendix for more examples.

In cases where solar charging is not adequate for keeping the battery above 3.7 V, it may be necessary to assist in powering the stations by swapping out the dead battery with a second fully charged replacement battery. For this, purchase a backup battery, LiPo battery charger, USB charging cable, and USB Wall Charger setup to be able to charge your backup battery whenever required for your particular situation.

Do not buy random battery packs or battery chargers on Amazon or from other vendors without checking with the EnviroDIY forum first, the majority of LiPo batteries made for radio controlled cars/aircraft have backwards polarity wires on the connectors, which will permanently damage the Mayfly Logger if you connect them and could become a potential fire hazard.

To ensure safety, be sure to only charge a battery while you are there to watch it. Keep the red charging circuit board away from any metal surfaces or liquids. Remove the battery from the charger as soon as possible after the green “done” light turns on.

The LiPo battery plugs into the Mayfly Data Logger in either one of the two JST connectors labeled LIPO BATT (Figure 8.2.6.2), but only connect ONE battery to the Mayfly at a time, and never connect two batteries at the same time (the spare jack is for connecting a jumper cable for supplying battery power to auxiliary devices in rare cases.

The battery will only fit in one direction and should not be forced to go the opposite way. 

You can verify the polarity by checking that the black wire is in line with the (-) sign and the red wire is in line with the (+) sign printed next to the white JST jacks. If the battery is forced in backwards, it could damage the mayfly and/or the battery.

When replacing the LiPo battery follow the steps listed below in Figure 8.2.6.3. Be sure to turn off the Mayfly using the main power switch before swapping batteries. Unplug the dead battery, connect the charged battery, and then turn the Mayfly back on with the main power switch. You should see the initial red-green LED blink pattern as the board starts up and is initialized.

8.2.7 Staff Gauge

The staff gauge is intended to serve as the master reference for stream depth at the EnviroDIY Monitoring Station location. The staff gauge will almost always measure a different depth than the CTD sensor simply because they are positioned at different locations in the stream.

For general reference and to confirm sensor or staff gauge data consistency, it is important to know the offset between the staff gauge and the sensor depth, i.e., the difference is between the water level as measured by the staff gauge and the water level as measured by the CTD sensor. This offset between staff gauge water depth and sensor water depth is also a key piece of information for use in developing the hydrologic (depth/discharge) rating curve.

Staff gauges installed in association with EnviroDIY Monitoring Stations are currently considered to be semi-permanent. They are set in the stream on ½” pipes which are generally stable and resilient; however, high flows in larger streams and rivers can damage the gauge by bending or breaking the pipe on which the gauge is mounted. If a staff gauge is bent or damaged it should be reset or replaced to the exact same depth using the the sensor/staff offset as the reference point.

View a guided video tutorial on how to build and install a staff gauge.

8.3 Data Patterns and Troubleshooting

Please see below for detailed information on data patterns and troubleshooting or consult the data patterns quick guides: 

• EnviroDIY Mayfly Data Quick Guide PA
• EnviroDIY Monitoring Stations – Data Patterns Quick Guide

8.3.1 Example Data

8.3.2 Data Patterns

Ecological Data Patterns

Sensor Fouling Data Patterns

Battery Level as a Diagnostic

8.3.3 Troubleshooting

The EnviroDIY Monitoring Station Troubleshooting Quick Guide is designed to be printed to provide troubleshooting tips while in the field. Further explanations can be found in Appendix 4: Troubleshooting.