Storm overflow register · Thames Water

Leatherhead sewage works: storm overflow spills 2025

Leatherhead sewage treatment works, run by Thames Water, has 1 monitored storm overflow discharging to River Mole. In 2025 it recorded 49 spills totalling 787 hours, against 82 spills and 1,243 hours in 2024. By hours spilling, it ranks 37 of 233 Thames Water works, where 1 spilled longest.

Works size: 46,809 population equivalent (LEATHERHEAD 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.

JanFebMarAprMayJunJulAugSepOctNovDecLeatherhead WwTW1 Jan 2025 16:45 GMT, 25.8 h5 Jan 2025 02:30 GMT, 119.5 h26 Jan 2025 14:30 GMT, 108.3 h31 Jan 2025 08:00 GMT, 43 h21 Feb 2025 23:45 GMT, 148.5 h28 Feb 2025 10:30 GMT, 15.3 h2 May 2025 20:15 GMT, 60 min7 Jun 2025 19:30 GMT, 30 min6 Jul 2025 16:15 GMT, 6 h19 Jul 2025 09:30 GMT, 11 h20 Oct 2025 08:30 GMT, 16.3 h23 Oct 2025 00:45 GMT, 23.3 h31 Oct 2025 21:30 GMT, 52.5 h23 Nov 2025 10:30 GMT, 15.3 h2 Dec 2025 22:45 GMT, 27.3 h4 Dec 2025 10:00 GMT, 19 h5 Dec 2025 10:15 GMT, 43.3 h7 Dec 2025 09:45 GMT, 18.8 h8 Dec 2025 11:00 GMT, 14.5 h9 Dec 2025 08:00 GMT, 18.3 h18 Dec 2025 13:45 GMT, 60.3 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.

0200k400k600kJan 2025: 270 h spilling ≈ 216,151 m³ (range 86,098–542,656 m³)JanFeb 2025: 189 h spilling ≈ 151,587 m³ (range 60,380–380,564 m³)FebMar 2025: 1.8 h spilling ≈ 1,444 m³ (range 575–3,624 m³)MarApr 2025: 0.0 h spilling ≈ 0.0 m³ (range 0.0–0.0 m³)AprMay 2025: 1.0 h spilling ≈ 802 m³ (range 319–2,014 m³)MayJun 2025: 0.5 h spilling ≈ 401 m³ (range 160–1,007 m³)JunJul 2025: 17 h spilling ≈ 13,635 m³ (range 5,431–34,231 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: 42 h spilling ≈ 33,686 m³ (range 13,418–84,570 m³)OctNov 2025: 65 h spilling ≈ 52,293 m³ (range 20,830–131,285 m³)NovDec 2025: 201 h spilling ≈ 161,372 m³ (range 64,278–405,130 m³)Dec
Cubic metres (m³), estimate. Hours are measured by the event duration monitor.

Longest single spills

Started (GMT)OverflowDurationEstimated volume
21 Feb 2025, 23:45Leatherhead WwTW6.2 days47,442 – 299,015 m³
5 Jan 2025, 02:30Leatherhead WwTW5.0 days38,177 – 240,621 m³
26 Jan 2025, 14:30Leatherhead WwTW4.5 days34,583 – 217,969 m³
18 Dec 2025, 13:45Leatherhead WwTW2.5 days19,248 – 121,317 m³
31 Oct 2025, 21:30Leatherhead WwTW2.2 days16,772 – 105,712 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 estimate631,370 m³range 251,488 – 1.6 million m³
In litres631.4 millionrange 251.5 million – 1.6 billion L
Olympic swimming pools253at 2,500 m³ each
Organic load, as people's raw sewage947,055person-days of untreated BOD

Assumed spill rate while spilling: 88.7 – 559.3 L/s (central 222.8 L/s), from a dry-weather flow of 88.7 L/s.

Pollutant releasedLowCentralHighConcentration used (low / typical / high)
BOD₅ (organic load) 10,060 kg56,823 kg317,016 kg 40 / 90 / 200 mg/L
Low/high: Europe range, Ellis & Jenkins 2005; typical: UK, Ellis & Jenkins 2005 (both via botturi)
Suspended solids 26,406 kg268,332 kg1.1 million kg 105 / 425 / 721 mg/L
Low/high: Europe range; typical: UK, Ellis & Jenkins 2005 (via botturi)
Ammonium-N 478 kg3,978 kg14,741 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 302 kg1,642 kg8,559 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 25.1 trillion organisms631.4 trillion organisms1.6 × 10¹⁶ 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.

Leatherhead WwTW

Storm tank at sewage works · discharges to River Mole

Spills 2025
49 (787 hours) · down 40% on 2024
Spills 2024
82 (1,243 hours)
Long-term average
67.9 spills a year (monitored since 2019)
Monitor uptime
100% of the year
High-spill reason (company)
Not asset maintenance - Hydraulic capacity
Investigation
Env Act (SODRP) investigation ongoing
Improvement
No improvement action in reporting period
WFD catchment
Mole - Leatherhead to Hersham (GB106039017623)
Outlet location
TQ1471058030 (OS grid reference) · View on Apple Maps
EA ID / permit
TWL00262 · CTCR.1780 · company name: Leatherhead STW

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 Thames 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.