The summary above says what has to happen. This says how, with the numbers that decide whether it works.
1 · Put the intake upstream and the outfall downstream of everyone
Physically, absolutely, and with a margin. Take water from above the settlement; discharge below every household, and below your neighbours, not just below your own boundary.
Define a protection zone around the intake in writing: no latrines, no burials, no livestock, no workshops and no waste within it, enforced by the health authority. Broad Street in 1854 is the canonical lesson — one pump, contaminated by one cesspit a metre away, killed hundreds in ten days. The failure is almost never the treatment works; it is a pipe or a pit somebody put in the wrong place.
✓ Check: Walking upstream from the intake for a kilometre finds no latrine, cesspit, midden, burial or animal pen, and the zone is marked on the ground and on paper.
2 · Filter, then disinfect — and measure the disinfection
Slow sand filtration takes out turbidity and most of the pathogen load: 0.15–0.35 mm effective grain size, a bed of at least 60 cm, 0.1–0.4 m³ per m² per hour, ripened 2–3 weeks. See the slow sand filter.
Then chlorinate, which is the step that closes the gap on viruses. Aim for a free chlorine residual of at least 0.5 mg/l after 30 minutes of contact, at pH below 8 where chlorine is far more effective, and at least 0.2 mg/l at the furthest tap as the evidence that nothing has been added along the way. Turbidity must be below 1 NTU first — chlorine spends itself on suspended matter.
✓ Check: Residual chlorine measured at the tap furthest from the works reads above 0.2 mg/l, and turbidity into the chlorine contact tank is below 1 NTU.
3 · Keep the mains under pressure, always
An intermittent, unpressurised supply sucks groundwater in at every joint — and in a settlement with any sanitation problem, that groundwater is sewage. A pipe is only a barrier while the water in it is pushing outward.
Hold a minimum of about 15 m of head (1.5 bar) at the highest tap, from a service reservoir or a tower sized for at least a day's demand so pumps stopping does not mean pressure stopping. Chlorinate to leave a residual through the whole network. Fix leaks as contamination events rather than as water losses, and never let a repaired main back into service without flushing and disinfecting it.
✓ Check: Pressure logged at the worst point in the network stayed above 1.5 bar for a month, including during every pump stoppage.
4 · Build sewers that clean themselves
A sewer that silts becomes a blocked sewer becomes sewage in the street. The design rule is velocity, not size: at least 0.6–0.75 m/s at the daily flow, which for a small foul sewer means a steady fall — typically between 1 in 60 and 1 in 150 for a 150 mm pipe, depending on flow.
Bigger is worse: an oversized pipe runs shallow and slow. Egg-shaped brick sections hold velocity at low flow, which is why the Victorian interceptors were built that way. Put access chambers at every junction, every change of direction and every 50–100 m, and ventilate the system — sewer gas is explosive and, in a confined chamber, lethal.
✓ Check: Every reach meets its velocity at the measured dry-weather flow, and opening any chamber shows flowing sewage with no standing silt.
5 · Treat the sewage instead of relocating it
Untreated discharge exports the epidemic downstream to someone who did nothing to earn it.
- Screening and grit removal first, or everything downstream fills with rag and sand.
- Primary settlement — 2 hours or so of quiet retention removes perhaps a third of the oxygen demand as sludge.
- Biological treatment — a trickling filter of 40–60 mm stone with rotating distributors, or activated sludge with air blown in. This is where most of the work happens, and it is alive: it needs feeding steadily and it dies if shock-loaded or poisoned with trade waste.
- Final settlement, then discharge to water with enough flow to dilute what remains.
Judge it by measurement: falling oxygen demand and no sewage fungus or dead fish below the outfall.
✓ Check: The effluent is clear and odourless, and the river below the outfall supports the same life as the river above it.
6 · Recover the nutrients, carefully
Treated sludge returns phosphate and nitrogen to farmland, which matters enormously before synthetic nitrogen — and phosphate never stops mattering, because there is no synthetic route to it at all.
But treat it first: digest the sludge anaerobically at about 35 °C for 15–30 days, which cuts pathogens sharply and yields methane worth burning, or compost it hot at 55 °C for several days. Keep industrial waste out of the sewers that feed it — heavy metals from plating and tanning make sludge permanently unusable on land, and that decision is irreversible. Apply to arable, not to salad crops, and observe a waiting period before harvest.
✓ Check: Sludge going to farmland has been digested or hot-composted with the temperature and time recorded, and no trade effluent discharges to that catchment untreated.
7 · Make it a public function with power to compel connection
This never happens voluntarily. Every historical case required law, taxation and enforcement, because the household that must pay to connect gets a benefit that is mostly enjoyed by its neighbours.
So: a duty on the authority to provide, a duty on the householder to connect within a stated period, a charge levied on all rather than on users, and a power to do the work and recover the cost where someone refuses. Fund maintenance in the same law as construction — the commonest failure in the record is a works built by a grant with no revenue behind its operating cost, silted up within a decade. See the first public good.
✓ Check: Every dwelling in the served area is connected, and the maintenance budget is a standing line in the accounts rather than an appeal.
8 · Monitor continuously, because failure is silent
Most failures give no sign until there is an outbreak. A schedule, written and audited:
- Daily — chlorine residual at several points, turbidity, pressure.
- Weekly — bacteriological samples from the network. The standard is no E. coli in 100 ml, and a single positive is an incident, not a statistic.
- Continuously — flow and level alarms at the works.
- After every repair or burst — flush, disinfect, and sample before restoring supply.
Publish the results, including the failures, and keep them for years so trends are visible. Test the water; never assume it.
✓ Check: A year of daily residual and weekly bacteriological results exists with no unexplained gaps, and every positive sample has a written investigation against it.