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Routine seasonal sampling in the River Lark catchment revealed a significant swine‑derived pollution event. Using continuous water‑quality monitoring, automated microsamplers, and environmental DNA (eDNA) microbial source tracking (MST), investigators pinpointed when the pollution occurred, where it originated, and who was responsible. This blended approach provided both the timing and the biological proof needed to resolve a complex multi‑source catchment.

Fourteen sites. Multiple potential pollution sources. The key question: when does pollution occur and how do you prove it?


Project Overview

The River Lark project deployed fourteen monitoring sites along a 60 km stretch of the Suffolk catchment. Each site captured data every 15 minutes for:

  • Temperature
  • pH
  • Dissolved oxygen (DO)
  • Turbidity
  • Toxic ammonia (NH₃)

Two automated microsamplers were installed at each site. Triggered by ammonia spikes, they collected water samples at the exact moment a pollution event occurred. Samples were preserved and later analysed for eDNA, enabling microbial source tracking (MST) to determine the biological origin of contamination.

This blended approach provided both timing and proof, identifying not only when pollution happened, but where it came from.

Baseline sampling showed:

  • Trace human DNA across the catchment
  • Ruminant markers at several sites
  • No significant swine or bovine DNA

Then the seasons changed — and so did the data.


A Sudden Spike at Tollgate Bridge

Image 1: Map to show monitored sites in Bury St Edmunds

At Tollgate Bridge, a control site upstream of a sewage treatment plant, enterococci levels suddenly surged to approximately 41,000 copies per 100 mL — four times higher than any previous reading.

Historically, this location showed elevated or unsafe readings (<1,000 copies per 100 mL), but nothing of this magnitude.

Image 2: Enterococcus Spike at Tollgate

Image 3: Table showing Thresholds for Enterococci

This result demanded immediate investigation. Without MST, the spike would remain unexplained and open to dispute. Elevated indicator bacteria alone cannot distinguish between:

  • Agricultural runoff
  • Failing septic systems
  • Wildlife
  • Wastewater infrastructure

In mixed‑use catchments, this uncertainty stalls action. microbial source tracking (MST) changes that. eDNA analysis revealed the contamination was swine‑derived.

Image 4: Elevated Enterococcus Markers Shown in Seneye Sensors Dashboard

Sensor data also showed:

  • Repeated turbidity spikes
  • A drop in dissolved oxygen
  • A decrease in pH

Image 5: Seneye Sensor and Microsamplers at Tollgate Bridge

Image 6: Seneye Sensor and Microsamplers at Tollgate Bridge


Tracing the Source Upstream

With 13 additional monitoring points, the team traced the signal upstream. At Southgate, upstream of Tollgate:

  • Swine markers detected
  • Enterococci: 1,386 copies per 100 mL

The next upstream site with pollution was Sicklesmere.

At Sicklesmere (400 m downstream of a CSO), historical data typically showed:

  • Elevated enterococci and E. coli linked to human sources
  • Occasional ruminant markers
  • Generally acceptable physicochemical water quality

Image 7: Water Quality Overview from Tollgate Bridge

As winter progressed, the eDNA profile shifted dramatically.

  • Early December: swine markers appeared (low copy numbers)
  • January: swine DNA surged to 15,175 copies per 100 mL
    • E. coli: 311 copies per 100 mL
    • Enterococci: 5,985 copies per 100 mL

Image 8: e.Coli Spike at Sicklesmere

Image 9: Enterococcus Spike at Sicklesmere

Image 10: Seneye Sensor Dashboard Showing Sources of Contamination

Downstream at Penny’s Bridge, no swine markers were detected.

Image 11: Map to show Sites Swine Markers were Detected

By comparing samples taken within hours of each other, the team narrowed the pollution source from a 15 km search area to less than 2 km.


Actionable Intelligence for the Catchment Partnership

The River Lark Catchment Partnership investigated potential pig farming operations within the narrowed corridor.

A volunteer and former agricultural chemist identified a likely source:

  • An outdoor pig unit visible on satellite imagery
  • Pigs had recently been relocated closer to the river
  • The land sloped directly toward the watercourse
  • A clear runoff pathway existed

Without continuous monitoring, MST, and distributed sensors, this event would likely have gone undetected or misattributed.

Instead, the system provided:

  • Early warning of contamination
  • Species‑level source attribution
  • Rapid spatial narrowing
  • Evidence‑based insight for targeted investigation
  • Identification of a high‑risk agricultural runoff pathway

The Bigger Picture

Routine seasonal sampling didn’t just collect data — it revealed a hidden pollution event and translated it into action.

By combining:

  • Real‑time sensing
  • Automated microsamplers
  • eDNA‑based microbial source tracking
  • Catchment‑scale sensor networks

the project transformed reactive water‑quality testing into proactive catchment intelligence.

From baseline stability to pinpointing a swine pollution event within a 2 km stretch — and tracing it to a specific land‑use change — the River Lark project demonstrates the power of continuous, high‑resolution environmental monitoring to protect river health, support targeted enforcement, and safeguard public safety.