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Water-quality monitoring / Methods & evidence

Water quality,
across space
and time.

Water-quality monitoring with an uncrewed surface vessel (USV) brings measurements to different locations along a survey route. It adds spatial context to the observations that water managers and researchers use to understand a waterway.

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Different methods.
A fuller picture.

A route through the water answers a different question from a sensor fixed in one place. Mobile surveys help examine variation between locations. Fixed instruments can record changes at a location over longer periods. Collected samples allow laboratory analysis of selected substances or organisms.

For canal water-quality surveys, these methods can work together. A survey may highlight a stretch that warrants more detailed sampling; a fixed station may provide the time series needed to put that survey in context.

Mobile USV surveys

Measurements at multiple locations along a route. Readings are collected sequentially, so time as well as position matters when comparing them.

Fixed monitoring

Repeated observations at an instrumented location. Useful for understanding changes over time, while representing the conditions at that site.

Sample collection & laboratory analysis

Samples taken under a defined protocol for specific analyses. Appropriate methods are needed to investigate particular contaminants or microorganisms.

Autonomous water monitoring does not remove the need for a sampling strategy, instrument checks or careful interpretation. Brief events can occur between surveys, and surface readings do not describe conditions at every depth.

Understanding a survey

Five ways to read
the water.

These are the parameters illustrated in our mission preview. The descriptions explain their environmental meaning; they do not specify Ridley’s installed hardware or measurement accuracy.

Dissolved oxygenmg/L

Fish and other aquatic organisms depend on dissolved oxygen. Changes along the canal reveal where oxygen availability differs.

USGS: dissolved oxygen and water
Temperature°C

Temperature shapes aquatic habitats and how much oxygen water can hold. A spatial view reveals warmer and cooler stretches.

USGS: temperature and water
pHpH

A pH of 7 is neutral. Values below 7 are acidic; values above it are basic. Local changes add context to water-quality investigations.

USGS: ph and water
ConductivityµS/cm

Dissolved ions, including salts, affect conductivity. Changes help guide further sampling, without identifying a specific pollutant.

USGS: conductivity and water
TurbidityFNU

Suspended material scatters light. Mapping turbidity reveals differences in cloudiness and helps locate areas for closer investigation.

USGS: turbidity and water

Parameters provide clues about conditions. They do not, by themselves, identify pathogens, toxins or a pollution source. Turbidity units depend on the instrument’s optical method; FNU is the unit used in our example.

Research & sources / Reviewed 11 September 2026

Why closer observation
matters.

These five findings describe different populations, locations and periods. They provide context for the monitoring need; they are not a single trend or results from a Ridley survey.

80% of surveyed small waters scored moderate or poor for water quality.

3,200+ ditches, canals, ponds and other small waters in the Netherlands.

The 2023 Vang de Watermonsters citizen-science survey involved 772 trained volunteers. NIOO-KNAW reports that 80% of the sampled waters scored moderate or poor. This describes the surveyed sites, not a census of every Dutch waterway.

NIOO-KNAW · 2023Water quality in Dutch small waters remains below standard

60.4% of EU surface waters fell short of good ecological status or potential.

2021 assessment · rivers, lakes, transitional and coastal waters in 25 EU countries.

The EEA reports that 39.6% reached good or high ecological status or potential, leaving approximately 60.4% below that level. The electronically reported dataset covers 25 EU Member States, excluding Finland and Hungary. Ecological status describes ecosystem condition; it is not a drinking-water or bathing-water safety rating.

European Environment Agency · 2021 dataEcological status of surface waters in Europe

18.6% decline in deep-water oxygen across the temperate lakes studied.

Estimated change from 1980 to 2017 · long-term lake research.

The study analysed 45,148 temperature and oxygen profiles from 393 temperate lake and reservoir basins. Its long-term late-summer analysis estimated an 18.6% decline in deep-water dissolved oxygen from 1980 to 2017; the deep-water trend subset contained 191 lakes. The graphic indexes the reported change to 100 in 1980. It is not a measured annual series or a claim about Amsterdam canals.

Jane et al. · Nature · 2021Widespread deoxygenation of temperate lakes

>320k kilometres of ditches across the Netherlands.

A vast network whose ecological condition remains largely out of view, according to a 2025 national study.

Haskoning’s September 2025 report describes more than 320,000 km of Dutch ditches. These small waters often fall outside designated Water Framework Directive water bodies, leaving major gaps in knowledge of their ecological condition. The report recommends expanding monitoring. This is the extent of the ditch network, not a measured length of unmonitored water or a claim that every ditch is navigable by Ridley.

Haskoning · 2025Trendanalyse waterkwaliteit sloten — for Natuur & Milieu

≈20% of Dutch sewer-overflow sites had monitoring for spill frequency.

September 2024 government response · spill monitoring does not measure the impact on surrounding water.

The Minister of Infrastructure and Water Management reported spill-frequency monitoring at approximately 20% of sewer-overflow locations. The national total cited was 13,000 sites, based on 2016 inventory data. The response distinguishes this from water-quality monitoring: water boards take regular surface-water measurements, with occasional monitoring of particular sites or events. Overflows can cause short-lived local oxygen depletion and fish deaths, but account for only about 0.4% of national nutrient emissions to surface water. The 20% is a dated monitoring estimate, not the share of polluted water or current coverage.

Dutch Government · 2024Parliamentary answers on water quality, questions 10–11

Useful data starts
before the route.

A spatial picture is only as useful as its underlying observations. The survey design should identify what will be measured, how the instruments will be checked, and how the measurements will inform a decision.

  • Define the question. Choose parameters and locations appropriate to the waterway and the decision at hand.
  • Document the method. Record calibration, measurement depth, sensor response and relevant operating conditions.
  • Keep time and position. Retain timestamps and coordinates alongside the readings.
  • Compare like with like. Use comparable routes and protocols, and account for differences in weather and time of day.
  • Follow up when needed. Use reference measurements or targeted sampling to investigate unexpected observations.

Patara’s Ridley project applies this spatial perspective to the design of a compact autonomous surface vessel. We welcome pilot discussions with organisations exploring how mobile sensing could complement their monitoring work.

Explore the Ridley USV project

Start with your waterway

What would a better
survey help you see?

Tell us about the waterway, the questions you need to answer, and the decisions the measurements should support.

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