Storm overflow register · Wessex Water

Lytchett Minster sewage works: storm overflow spills 2025

Lytchett Minster sewage treatment works, run by Wessex Water, has 1 monitored storm overflow discharging to Lytchett Bay(E). In 2025 it recorded 13 spills totalling 163 hours, against 28 spills and 305 hours in 2024. By hours spilling, it ranks 169 of 242 Wessex Water works, where 1 spilled longest.

Works size: 8,753 population equivalent (LYTCHETT MINSTER 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.

JanFebMarAprMayJunJulAugSepOctNovDecLytchett Minster STW5 Jan 2025 07:09 GMT, 35.9 h6 Jan 2025 19:04 GMT, 5.5 h26 Jan 2025 22:56 GMT, 40.1 h24 Feb 2025 06:31 GMT, 16.9 h20 Oct 2025 15:06 GMT, 8 h2 Dec 2025 00:26 GMT, 6.3 h9 Dec 2025 02:12 GMT, 1 min9 Dec 2025 02:12 GMT, 23 h18 Dec 2025 12:31 GMT, 27.1 h

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.

010k20k30k40kJan 2025: 82 h spilling ≈ 12,223 m³ (range 4,869–30,687 m³)JanFeb 2025: 17 h spilling ≈ 2,535 m³ (range 1,010–6,363 m³)FebMar 2025: 0.0 h spilling ≈ 0.0 m³ (range 0.0–0.0 m³)MarApr 2025: 0.0 h spilling ≈ 0.0 m³ (range 0.0–0.0 m³)AprMay 2025: 0.0 h spilling ≈ 0.0 m³ (range 0.0–0.0 m³)MayJun 2025: 0.0 h spilling ≈ 0.0 m³ (range 0.0–0.0 m³)JunJul 2025: 0.0 h spilling ≈ 0.0 m³ (range 0.0–0.0 m³)JulAug 2025: 0.0 h spilling ≈ 0.0 m³ (range 0.0–0.0 m³)AugSep 2025: 0.0 h spilling ≈ 0.0 m³ (range 0.0–0.0 m³)SepOct 2025: 8.0 h spilling ≈ 1,200 m³ (range 478–3,012 m³)OctNov 2025: 0.0 h spilling ≈ 0.0 m³ (range 0.0–0.0 m³)NovDec 2025: 56 h spilling ≈ 8,444 m³ (range 3,363–21,198 m³)Dec
Cubic metres (m³), estimate. Hours are measured by the event duration monitor.

Longest single spills

Started (GMT)OverflowDurationEstimated volume
26 Jan 2025, 22:56Lytchett Minster STW1.7 days2,398 – 15,111 m³
5 Jan 2025, 07:09Lytchett Minster STW1.5 days2,145 – 13,517 m³
18 Dec 2025, 12:31Lytchett Minster STW1.1 days1,616 – 10,185 m³
9 Dec 2025, 02:12Lytchett Minster STW23.0 h1,372 – 8,648 m³
24 Feb 2025, 06:31Lytchett Minster STW16.9 h1,012 – 6,376 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 estimate24,416 m³range 9,726 – 61,298 m³
In litres24.4 millionrange 9.7 million – 61.3 million L
Olympic swimming pools9.8at 2,500 m³ each
Organic load, as people's raw sewage36,625person-days of untreated BOD

Assumed spill rate while spilling: 16.6 – 104.6 L/s (central 41.7 L/s), from a dry-weather flow of 16.6 L/s.

Pollutant releasedLowCentralHighConcentration used (low / typical / high)
BOD₅ (organic load) 389 kg2,197 kg12,260 kg 40 / 90 / 200 mg/L
Low/high: Europe range, Ellis & Jenkins 2005; typical: UK, Ellis & Jenkins 2005 (both via botturi)
Suspended solids 1,021 kg10,377 kg44,196 kg 105 / 425 / 721 mg/L
Low/high: Europe range; typical: UK, Ellis & Jenkins 2005 (via botturi)
Ammonium-N 18 kg154 kg570 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 12 kg63 kg331 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 972.6 billion organisms24.4 trillion organisms613.0 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.

Lytchett Minster STW

Storm tank at sewage works · discharges to Lytchett Bay(E)

Spills 2025
13 (163 hours) · down 54% on 2024
Spills 2024
28 (305 hours)
Long-term average
15.0 spills a year (monitored since 2017)
Monitor uptime
100% of the year
Investigation
Env Act (SODRP) investigation ongoing, UWWTR investigation ongoing
Improvement
Env Act (SODRP) improvement ongoing
Bathing water
Poole Harbour Rockley Sands
Shellfish water
Poole Bay; Poole Harbour North; Poole Harbour South; Poole Harbour West
WFD catchment
POOLE HARBOUR (GB520804415800)
Outlet location
SY9685092300 (OS grid reference) · View on Apple Maps
EA ID / permit
WXW00668 · 401242 · company name: LYTCHETT MINSTER LYTCHETT BAY STORM TANK

How the estimate works

  1. 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].
  2. 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.
  3. Low spill rate = DWF. This is the method used by Giakoumis & Voulvoulis (2026), which they note likely underestimates storm loads [G&V].
  4. 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.
  5. Volume = spill rate × hours spilling, with hours taken from the event duration monitor.
  6. 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

  1. EA: Water companies – environmental permits for storm overflows and emergency overflows
  2. EA: Water resources 2024 to 2025 – per capita consumption
  3. HBF: Foul sewer design – historic conventions (citing Escritt 1984 on infiltration)
  4. Giakoumis & Voulvoulis (2026), Environ. Sci.: Water Res. Technol., doi:10.1039/D5EW00860C
  5. Botturi et al. (2021), Crit. Rev. Environ. Sci. Technol. 51:1585 – CSO quality review, Table 2
  6. US EPA (2004) Report to Congress on CSOs and SSOs, chapter 4
  7. Urban Waste Water Treatment Directive, Article 2(6): 1 p.e. = 60 g BOD5/day
  8. Olympic-size swimming pool: 2,500 m³ at the nominal 2 m depth

← 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.