Ryhall sewage works: storm overflow spills 2025

Ryhall sewage treatment works, run by Anglian Water, has 1 monitored storm overflow discharging to River Gwash. In 2025 it recorded 62 spills totalling 706 hours, against 81 spills and 1,002 hours in 2024. By hours spilling, it ranks 22 of 419 Anglian Water works, where 1 spilled longest.

Works size: 2,257 population equivalent (RYHALL STW, UWWTD 2018). Used for the spill volume estimate.

Every spill in 2025

Each blue mark is one spill, placed by when it started and sized by how long it lasted. Hover over a mark for the date and duration.

Estimated spill volume by month, 2025

Hours spilling each month × the estimated spill rate for a works of this size. The bars are central estimates and the whiskers show the low–high range. Method.

Cubic metres (m³), estimate. Hours are measured by the event duration monitor.

Longest single spills

Started (GMT)	Overflow	Duration	Estimated volume
9 Dec 2025, 00:00	Ryhall Water Recycling Centre	1.0 days	370 – 2,330 m³
6 Dec 2025, 00:00	Ryhall Water Recycling Centre	1.0 days	370 – 2,330 m³
19 Dec 2025, 04:38	Ryhall Water Recycling Centre	18.0 h	277 – 1,744 m³
5 Dec 2025, 06:24	Ryhall Water Recycling Centre	17.6 h	271 – 1,709 m³
7 Dec 2025, 07:44	Ryhall Water Recycling Centre	16.3 h	251 – 1,579 m³

Estimated 2025 spill volume and pollution

Estimate, not a measurement. Monitors record how long an overflow spills, not how much. This calculator back-calculates a spill rate from the size of the works, using the Environment Agency's permit formulae, and multiplies it by published storm-sewage concentrations. How it works.

Volume, central estimate27,318 m³range 10,881 – 68,583 m³

In litres27.3 millionrange 10.9 million – 68.6 million L

Olympic swimming pools11at 2,500 m³ each

Organic load, as people's raw sewage40,977person-days of untreated BOD

Assumed spill rate while spilling: 4.3 – 27.0 L/s (central 10.7 L/s), from a dry-weather flow of 4.3 L/s.

Pollutant released	Low	Central	High	Concentration used (low / typical / high)
BOD₅ (organic load)	435 kg	2,459 kg	13,717 kg	40 / 90 / 200 mg/L Low/high: Europe range, Ellis & Jenkins 2005; typical: UK, Ellis & Jenkins 2005 (both via botturi)
Suspended solids	1,143 kg	11,610 kg	49,449 kg	105 / 425 / 721 mg/L Low/high: Europe range; typical: UK, Ellis & Jenkins 2005 (via botturi)
Ammonium-N	21 kg	172 kg	638 kg	1.9 / 6.3 / 9.3 mg/L Low: Germany, Brombach 2005; typical/high: Paris range 3.3–9.3 midpoint and top, Gasperi 2012 (via botturi); no UK value found
Total phosphorus	13 kg	71 kg	370 kg	1.2 / 2.6 / 5.4 mg/L Low/high: Paris, Gasperi 2012; typical: Slovakia (via botturi). UK figure of 10 mg/L treated as an outlier
E. coli	1.1 trillion organisms	27.3 trillion organisms	685.8 trillion organisms	10,000 / 100,000 / 1.0 million per 100 mL Median range at CSO and retention-tank outlets, Stott et al. 2018 (via botturi); typical = log midpoint

Low combines the low spill rate with low concentrations, and high combines high with high, so the true figure is very likely inside the range. Long spills become more diluted as they go on, so the central figure tends to overstate the load of long events. The calculator does not estimate the effect on the receiving water, which depends on river flow or tide at the time of the spill.

Ryhall Water Recycling Centre

Storm tank at sewage works · discharges to River Gwash

Spills 2025: 62 (706 hours) · down 23% on 2024
Spills 2024: 81 (1,002 hours)
Long-term average: 42.0 spills a year (monitored since 2022)
Monitor uptime: 100% of the year
High-spill reason (company): Performance - Asset configuration (e.g. PS/rising main/storm tanks)
Investigation: Env Act (SODRP) investigation ongoing, Operational investigation ongoing
Improvement: Operational improvement ongoing
WFD catchment: Gwash (GB105031050610)
Outlet location: TF0404010700 (OS grid reference) · View on Apple Maps
EA ID / permit: AWS01084 · AW5NF5213 · company name: RYHALL STW

How the estimate works

Dry-weather flow (DWF) = population × water use per person × (1 + infiltration). Water use is 136.5 L per person per day, England's per-capita consumption for 2024–25 [EA]. Infiltration of groundwater into sewers is taken as 0–40% of that flow [Escritt, via HBF]. The Environment Agency defines DWF as PG + I + E [EA].
Population. The size of each works comes from the load entering it as reported under the Urban Waste Water Treatment Directive, in population equivalents (1 p.e. = 60 g of BOD a day) [UWWTD]. We treat population equivalent as population. That overstates flow where trade effluent adds load, and no official source links the two. Works serving fewer than 2,000 p.e. are not reported, so their size has to be entered by hand.
Low spill rate = DWF. This is the method used by Giakoumis & Voulvoulis (2026), which they note likely underestimates storm loads [G&V].
High spill rate = Formula A − flow to full treatment = (DWF + 1360P) − 3DWF. This is the largest flow the permit expects the storm tanks to handle before it passes on to treatment or overflows [EA]. The central rate is the geometric mean of the low and high rates.
Volume = spill rate × hours spilling, with hours taken from the event duration monitor.
Pollution = volume × published storm-sewage concentrations [Botturi et al.] [US EPA]. Organic load is also shown as person-days of untreated sewage at 60 g of BOD per person per day [UWWTD].

What this cannot tell you. It gives no real flow for any single spill, and no effect on the river or sea, which depends on the flow, tide and the other pressures on the water at the time. It gives no figure for spills from overflows on the sewer network, which serve catchments of unknown size. It is a way to put hours into rough physical terms, not a substitute for flow monitoring.

Sources

← All Anglian Water works · Contains Environment Agency data licensed under the Open Government Licence v3.0. Spill start and stop times: © Environment Agency copyright and/or database right 2026. All rights reserved. They are water-company data and have not been verified by the Environment Agency. Works size: EEA Waterbase UWWTD. How to read the data.