Furthermore, animals have to drink and are known to visit water holes. This raises several concerns, 1) Animals are not very mindful of their toilet etiquette and 2) Predators will sometimes use water holes as a place of attack. If we were desperate, (dying of thirst) and had no way to purify the water, first we really should ask ourselves how we got ourselves into such a situation, then we would have no choice but to drink the water in hopes that we are rescued before the water borne disease kills us. Think outside the box, is there a way to get a makeshift bowl (wood, vegetation) and use hot rocks to boil the water. Is there any material around, bamboo etc that can be used to slowly bring the water to a boil. Build a multiple stage filter using sand, charcoal and sphagnum moss which has been known to contain some levels of iodine. If all that fails then we would be faced with the choice of drinking the untreated water. We know that moving water is preferable to standing water, but what can we do. We can walk around the water source, find the area with the least animal traffic and preferably a sandy shoreline. We can then dig a hole near the water deep enough to allow water to collect. The distance from the water source will have to be judged by the soil we are digging. The hope here is that the water will slowly seep into the hole and begin to collect while being "filtered" by the sand and rocks. At this point we have to get creative to get the water out. Perhaps make a straw out of natural materials or simply soak a bandana and squeeze it into our mouth. This would be a last resort and very risky.
• Snow: The energy it requires for your body to absorb the water from snow is high. Instead of eating the snow, melt it first. This can easily be done over a fire or with a camp stove. If those aren’t options, use the sun. Accelerate the process by chopping up ice and hanging it in a water bag in direct sunlight. If there’s no sun, use your body’s heat.
While the intermittent nature of sunlight and its variable intensity throughout the day makes PV efficiency prediction difficult and desalination during night time challenging, several solutions exist. For example, batteries, which provide the energy required for desalination in non-sunlight hours can be used to store solar energy in daytime. Apart from the use of conventional batteries, alternative methods for solar energy storage exist. For example, thermal energy storage systems solve this storage problem and ensure constant performance even during non-sunlight hours and cloudy days, improving overall efficiency.[13]

Drinking water sources are subject to contamination and require appropriate treatment to remove disease-causing agents. Public drinking water systems use various methods of water treatment to provide safe drinking water for their communities. Today, the most common steps in water treatment used by community water systems (mainly surface water treatment) include:
A nice feature of the Sawyer system is the benefit of using the same filter as a water treatment bottle, inline on a hydration pack, as an ultra light drink straw and attached to a faucet with the included faucet adaptor. If purchased with the faucet adaptor kit, it can be configured to drink straight from the tap during boil alerts or in areas of natural disasters such as floods, hurricanes, and earthquakes. The kit also provides hydration pack assembly kit for installing the inline filter on a hydration pack.
Direct contact membrane distillation (DCMD). Applicable to desalination. Heated seawater is passed along the surface of a hydrophobic polymer membrane. Evaporated water passes from the hot side through pores in the membrane into a stream of cold pure water on the other side. The difference in vapour pressure between the hot and cold side helps to push water molecules through.
The membranes used for reverse osmosis have a dense layer in the polymer matrix—either the skin of an asymmetric membrane or an interfacially polymerized layer within a thin-film-composite membrane—where the separation occurs. In most cases, the membrane is designed to allow only water to pass through this dense layer while preventing the passage of solutes (such as salt ions). This process requires that a high pressure be exerted on the high-concentration side of the membrane, usually 2–17 bar (30–250 psi) for fresh and brackish water, and 40–82 bar (600–1200 psi) for seawater, which has around 27 bar (390 psi)[8] natural osmotic pressure that must be overcome. This process is best known for its use in desalination (removing the salt and other minerals from sea water to produce fresh water), but since the early 1970s, it has also been used to purify fresh water for medical, industrial and domestic applications.
Bioremediation is a technique that uses microorganisms in order to remove or extract certain waste products from a contaminated area. Since 1991 bioremediation has been a suggested tactic to remove impurities from water such as alkanes, perchlorates, and metals.[26] The treatment of ground and surface water, through bioremediation, with respect to perchlorate and chloride compounds, has seen success as perchlorate compounds are highly soluble making it difficult to remove.[27] Such success by use of Dechloromonas agitata strain CKB include field studies conducted in Maryland and the Southwest region of the United States.[27][28][29] Although a bioremediation technique may be successful, implementation is not feasible as there is still much to be studied regarding rates and after effects of microbial activity as well as producing a large scale implementation method. 

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 addition of inorganic coagulants such as aluminum sulfate (or alum) or iron (III) salts such as iron(III) chloride cause several simultaneous chemical and physical interactions on and among the particles. Within seconds, negative charges on the particles are neutralized by inorganic coagulants. Also within seconds, metal hydroxide precipitates of the iron and aluminium ions begin to form. These precipitates combine into larger particles under natural processes such as Brownian motion and through induced mixing which is sometimes referred to as flocculation. Amorphous metal hydroxides are known as "floc". Large, amorphous aluminum and iron (III) hydroxides adsorb and enmesh particles in suspension and facilitate the removal of particles by subsequent processes of sedimentation and filtration.[6]:8.2–8.3