Almondsbury sewage works: storm overflow spills 2025

Almondsbury sewage treatment works, run by Wessex Water, has 1 monitored storm overflow discharging to Sandy Rhine Trib Chestle Pill. In 2025 it recorded 40 spills totalling 515 hours, against 86 spills and 1,276 hours in 2024. By hours spilling, it ranks 81 of 242 Wessex Water works, where 1 spilled longest.

Works size: 2,698 population equivalent (ALMONDSBURY 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
15 Dec 2025, 08:01	Almondsbury WwTW	5.6 days	2,488 – 15,680 m³
5 Jan 2025, 02:03	Almondsbury WwTW	2.9 days	1,290 – 8,130 m³
14 Nov 2025, 04:25	Almondsbury WwTW	2.4 days	1,043 – 6,577 m³
9 Dec 2025, 01:14	Almondsbury WwTW	1.9 days	845 – 5,325 m³
1 Dec 2025, 18:04	Almondsbury WwTW	1.3 days	588 – 3,706 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 estimate23,822 m³range 9,489 – 59,805 m³

In litres23.8 millionrange 9.5 million – 59.8 million L

Olympic swimming pools9.5at 2,500 m³ each

Organic load, as people's raw sewage35,732person-days of untreated BOD

Assumed spill rate while spilling: 5.1 – 32.2 L/s (central 12.8 L/s), from a dry-weather flow of 5.1 L/s.

Pollutant released	Low	Central	High	Concentration used (low / typical / high)
BOD₅ (organic load)	380 kg	2,144 kg	11,961 kg	40 / 90 / 200 mg/L Low/high: Europe range, Ellis & Jenkins 2005; typical: UK, Ellis & Jenkins 2005 (both via botturi)
Suspended solids	996 kg	10,124 kg	43,120 kg	105 / 425 / 721 mg/L Low/high: Europe range; typical: UK, Ellis & Jenkins 2005 (via botturi)
Ammonium-N	18 kg	150 kg	556 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	11 kg	62 kg	323 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	948.9 billion organisms	23.8 trillion organisms	598.1 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.

Almondsbury WwTW

Storm tank at sewage works · discharges to Sandy Rhine Trib Chestle Pill

Spills 2025: 40 (515 hours) · down 53% on 2024
Spills 2024: 86 (1,276 hours)
Long-term average: 63.0 spills a year (monitored since 2024)
Monitor uptime: 100% of the year
High-spill reason (company): Not Applicable - Ongoing investigation
Investigation: Env Act (SODRP) investigation ongoing, UWWTR investigation ongoing
Improvement: No improvement action in reporting period
WFD catchment: Chestle Pill (GB109054026650)
Outlet location: ST5990985033 (OS grid reference) · View on Apple Maps
EA ID / permit: WXW00078 · 010001 · company name: ALMONDSBURY STORM TANK

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 Wessex 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.