Storm overflow register · South West Water

Salcombe Regis sewage works: storm overflow spills 2025

Salcombe Regis sewage treatment works, run by South West Water, has 1 monitored storm overflow discharging to Salcombe Regis Stream. In 2025 it recorded 235 spills totalling 5,446 hours, against 366 spills and 8,773 hours in 2024. By hours spilling, it ranks 1 of 334 South West Water works, where 1 spilled longest.

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.

JanFebMarAprMayJunJulAugSepOctNovDecSalcombe Regis WwTW…1 Jan 2025 00:00 GMT, 995.7 h11 Feb 2025 11:41 GMT, 813.8 h17 Mar 2025 09:27 GMT, 42 min17 Mar 2025 10:10 GMT, 622.4 h12 Apr 2025 09:21 GMT, 108 min12 Apr 2025 11:59 GMT, 19.5 h13 Apr 2025 08:11 GMT, 2.1 h13 Apr 2025 10:59 GMT, 101 min13 Apr 2025 13:24 GMT, 261.5 h24 Apr 2025 10:57 GMT, 2329.4 h30 Jul 2025 12:22 GMT, 81 min30 Jul 2025 13:44 GMT, 196.7 h8 Aug 2025 11:40 GMT, 72.7 h29 Aug 2025 01:36 GMT, 2.3 h11 Nov 2025 19:09 GMT, 32.7 h13 Nov 2025 19:10 GMT, 52 h23 Nov 2025 03:17 GMT, 34.8 h3 Dec 2025 08:16 GMT, 41 min3 Dec 2025 16:02 GMT, 14 min19 Dec 2025 01:43 GMT, 63 min26 Dec 2025 21:47 GMT, 3.2 h

Hours spilling by month, 2025

0200400600800Jan 2025: 744 hours spillingJanFeb 2025: 672 hours spillingFebMar 2025: 744 hours spillingMarApr 2025: 716 hours spillingAprMay 2025: 744 hours spillingMayJun 2025: 720 hours spillingJunJul 2025: 744 hours spillingJulAug 2025: 238 hours spillingAugSep 2025: 0.0 hours spillingSepOct 2025: 0.0 hours spillingOctNov 2025: 119 hours spillingNovDec 2025: 5.1 hours spillingDec
Hours, measured by the event duration monitor.

Longest single spills

Started (GMT)OverflowDuration
24 Apr 2025, 10:57Salcombe Regis WwTW CSO97.1 days
1 Jan 2025, 00:00Salcombe Regis WwTW CSO41.5 days
11 Feb 2025, 11:41Salcombe Regis WwTW CSO33.9 days
17 Mar 2025, 10:10Salcombe Regis WwTW CSO25.9 days
13 Apr 2025, 13:24Salcombe Regis WwTW CSO10.9 days

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.

This works serves fewer than 2,000 people, or was not matched to a UWWTD report, so its size is not published. The population equivalent above is a placeholder of 1,000. Enter the population served if you know it.

Volume, central estimate93,316 m³range 37,170 – 234,273 m³
In litres93.3 millionrange 37.2 million – 234.3 million L
Olympic swimming pools37at 2,500 m³ each
Organic load, as people's raw sewage139,974person-days of untreated BOD

Assumed spill rate while spilling: 1.9 – 11.9 L/s (central 4.8 L/s), from a dry-weather flow of 1.9 L/s.

Pollutant releasedLowCentralHighConcentration used (low / typical / high)
BOD₅ (organic load) 1,487 kg8,398 kg46,855 kg 40 / 90 / 200 mg/L
Low/high: Europe range, Ellis & Jenkins 2005; typical: UK, Ellis & Jenkins 2005 (both via botturi)
Suspended solids 3,903 kg39,659 kg168,911 kg 105 / 425 / 721 mg/L
Low/high: Europe range; typical: UK, Ellis & Jenkins 2005 (via botturi)
Ammonium-N 71 kg588 kg2,179 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 45 kg243 kg1,265 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 3.7 trillion organisms93.3 trillion organisms2.3 × 10¹⁵ 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.

Salcombe Regis WwTW CSO

Inlet overflow at sewage works · discharges to Salcombe Regis Stream

Spills 2025
235 (5,446 hours) · down 36% on 2024
Spills 2024
366 (8,773 hours)
Long-term average
206.3 spills a year (monitored since 2022)
Monitor uptime
100% of the year
High-spill reason (company)
Not asset maintenance - hydraulic capacity
Investigation
Operational investigation completed
Improvement
Env Act (SODRP) improvement ongoing, Operational improvement completed
WFD catchment
Not part of a WFD catchment
Outlet location
SY14728839 (OS grid reference) · View on Apple Maps
EA ID / permit
SBB01043 · NRA-SW-1505 · company name: SALCOMBE REGIS STW_SO_SALCOMBE REGIS

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 South West 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.