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.
Countertop RO water systems are those systems that can be placed easily on the top of the Kitchen Table. These are designed for small families as they produce a small quantity of purified water. Countertop RO system is portable and inexpensive than most of other RO water filters. It is ideal for tenants who may not have permission to make changes in the house they live in.
Simply fill the provided container with water. Shake the container. Allow the filled container to stand for about an hour. This allows time for the water to become saturated with iodine. Add the iodine to your water container, adding the indicated amount of capfuls (it's about 1 capful to 1 quart). Shake the water container to ensure a proper mixture. Allow the container to sit 20-30 minutes. Afterwards the water is ready to drink.
Treatment with reverse osmosis is limited, resulting in low recoveries on high concentration (measured with electrical conductivity) and fouling of the RO membranes. Reverse osmosis applicability is limited by conductivity, organics, and scaling inorganic elements such as CaSO4, Si, Fe and Ba. Low organic scaling can use two different technologies, one is using spiral wound membrane type of module, and for high organic scaling, high conductivity and higher pressure (up to 90 bars) disc tube modules with reverse-osmosis membranes can be used. Disc tube modules were redesigned for landfill leachate purification, that is usually contaminated with high levels of organic material. Due to the cross-flow with high velocity it is given a flow booster pump, that is recirculating the flow over the same membrane surface between 1.5 and 3 times before it is released as a concentrate. High velocity is also good against membrane scaling and allows successful membrane cleaning.

Use sedimentation. When you don’t have access to anything that you can use to filter the water, you can remove large particulate from water by letting it settle. Collect the water in a bowl or jar. Leave the water to settle for one to two hours. During this time, heavier particles will sink to the bottom, and lighter material will float to the top.[3]

Household water treatment systems are composed of two categories: point-of-use and point-of-entryExternal (NSF). Point-of-entry systems are typically installed after the water meter and treat most of the water entering a residence. Point-of-use systems are systems that treat water in batches and deliver water to a tap, such as a kitchen or bathroom sink or an auxiliary faucet mounted next to a tap.

Ion exchange:[11] Ion exchange systems use ion exchange resin- or zeolite-packed columns to replace unwanted ions. The most common case is water softening consisting of removal of Ca2+ and Mg2+ ions replacing them with benign (soap friendly) Na+ or K+ ions. Ion exchange resins are also used to remove toxic ions such as nitrite, lead, mercury, arsenic and many others.

Plumbosolvency reduction: In areas with naturally acidic waters of low conductivity (i.e. surface rainfall in upland mountains of igneous rocks), the water may be capable of dissolving lead from any lead pipes that it is carried in. The addition of small quantities of phosphate ion and increasing the pH slightly both assist in greatly reducing plumbo-solvency by creating insoluble lead salts on the inner surfaces of the pipes.
The goals of the treatment are to remove unwanted constituents in the water and to make it safe to drink or fit for a specific purpose in industry or medical applications. Widely varied techniques are available to remove contaminants like fine solids, micro-organisms and some dissolved inorganic and organic materials, or environmental persistent pharmaceutical pollutants. The choice of method will depend on the quality of the water being treated, the cost of the treatment process and the quality standards expected of the processed water.
Radium Removal: Some groundwater sources contain radium, a radioactive chemical element. Typical sources include many groundwater sources north of the Illinois River in Illinois, United States of America. Radium can be removed by ion exchange, or by water conditioning. The back flush or sludge that is produced is, however, a low-level radioactive waste.
Whether you are on a backpacking trip or find yourself in an unplanned emergency situation our first goal is to locate water. Depending on the location this may prove more difficult than ensuring it's potability. Make sure you are familiar with water sources in the area you plan to travel. Looking at topographical maps is always a good idea. Depending on the dates of the map this could help you find water while backpacking. As with other areas of emergency preparedness, make sure to have a backup plan. Water sources can change with time and seasonal changes. Another important aspect of finding water is the lay of the land. Learning the elevational changes of the area and thinking which way the water would travel during a rain can be another way to locate a water source. For the scope of this article, we will assume that a source has been located.
As with any other filter type water purification method, careful attention has to be taken to pathogen/virus and chemicals size. During hurricane Katrina a lot of the water was contaminated with petroleum based chemicals from flooded cars. What is removed from the water is dependent on the filter pore size. However, it is difficult to beat the lightweight option that water purification straws and bottles provide for most situations.