Chlorine dioxide is a faster-acting disinfectant than elemental chlorine. It is relatively rarely used because in some circumstances it may create excessive amounts of chlorite, which is a by-product regulated to low allowable levels in the United States. Chlorine dioxide can be supplied as an aqueous solution and added to water to avoid gas handling problems; chlorine dioxide gas accumulations may spontaneously detonate.
A reverse osmosis filter is the do-it-all of water purification. The process is the only one that addresses both harmful microorganisms and pollutants at the same time. It works by forcing water under pressure through a membrane made of thin film composite, with a inner matrix of dense polymers. The result leaves purified water on one side of the membrane, and contaminants on the other side. The technology is reliable, but expensive and relatively cumbersome, and requires electricity to work. It is therefore a sound choice for use in fixed positions or by those who can afford to tow a small trailer with a small electrical generator around, but anyone on the move or without access to electricity needs to use other methods.

Cut the bottom of a plastic bottle off -- these can be found almost everywhere at no cost. Replace the bottle cap with a cheesecloth/fine cloth, tied on with a rubber band and secure. Place it on a cup, with the cloth facing towards the ground. Put fine sand, charcoal, coarse sand and rocks in the bottle in the order listed. Pour water inside. Capture the water that has now been purified.
In 1904, Allen Hazen showed that the efficiency of a sedimentation process was a function of the particle settling velocity, the flow through the tank and the surface area of tank. Sedimentation tanks are typically designed within a range of overflow rates of 0.5 to 1.0 gallons per minute per square foot (or 1.25 to 2.5 litres per square meter per hour). In general, sedimentation basin efficiency is not a function of detention time or depth of the basin. Although, basin depth must be sufficient so that water currents do not disturb the sludge and settled particle interactions are promoted. As particle concentrations in the settled water increase near the sludge surface on the bottom of the tank, settling velocities can increase due to collisions and agglomeration of particles. Typical detention times for sedimentation vary from 1.5 to 4 hours and basin depths vary from 10 to 15 feet (3 to 4.5 meters).[6]:9.39–9.40[7]:790–1[8]:140–2, 171