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The concentration of dissolved calcium, magnesium, and, to a lesser extent, manganese and ferrous iron ions in hard water is decreased by a water softener. These "hardness ions" have three main negative effects. The most obvious result of metal ions' reaction with soaps and calcium-sensitive detergents is the formation of a precipitate known as the "bathtub ring," which prevents the soaps from lathering. Additionally, the cleaning effect of detergent formulations is inhibited by the presence of "hardness ions." Second, hard deposits of calcium and magnesium carbonates often form on the surfaces of heat exchangers and pipes. The primary cause of this is the thermal breakdown of bicarbonate ions, though it can also occur to some degree even when they are not present. Water flow in pipes may be impeded by the ensuing accumulation of scale. The deposits in boilers serve as insulation, preventing heat from entering the water, lowering heating efficiency, and causing the metal boiler parts to overheat. This may cause the boiler in a pressurized system to fail. Third, galvanic corrosion, in which one metal corrodes preferentially when in contact with another type of metal when both are in contact with an electrolyte, can also result from the presence of ions in an electrolyte, in this case, hard water. However, because the sodium (or potassium) ions released during conventional water softening are far more electrolytically active than the calcium or magnesium ions they replace, galvanic corrosion should be greatly increased rather than decreased. Similarly, if there is any lead plumbing, softened water is probably much more plumbosolvent than hard water.
Sodium ions that are electrostatically bonded to the anionic functional groups of the polymeric resin exchange places with "hardness" ions in an ion-exchange resin used in conventional water softening devices. Ion-exchange capabilities are also exhibited by a class of minerals known as zeolites, which were extensively utilized in earlier water softeners. If the water comes from a well, either private or public, water softeners might be a good idea.
 How it operates:
The resin bed is traversed by the water to be treated. Positively charged metal ions are absorbed and bound by negatively charged resins. Divalent calcium and magnesium ions in the water exchange with the univalent hydrogen, sodium, or potassium ions that are initially present in the resins. Hardness ions take the place of hydrogen, sodium, or potassium ions that are released into the water as it flows through the resin column. More hydrogen, sodium, or potassium ions are released from the resin and into the water the "harder" the water. Additionally, some resins can be used to eliminate absorbed carbonate, bicarbonate, and sulfate ions as well as hydroxyl ions. It is possible to have both kinds of resin in one water softener.
Restoration:
These resins gradually lose their efficacy as they accumulate unwanted cations and anions, necessitating regeneration. Regeneration is typically accomplished by passing concentrated brine—typically sodium chloride or potassium chloride—or a hydrochloric acid solution through them if a cationic resin is used (to remove calcium and magnesium ions). A solution of potassium hydroxide (lye) or sodium hydroxide is used for anionic resins. The majority of regeneration-related salts are flushed out of the system and may end up in the soil or sewer. The environment may suffer from these processes, particularly in arid areas. Some jurisdictions forbid this kind of release and mandate that users either use a commercial service company or dispose of the spent brine at an authorized location. To reduce the frequency of regeneration, the majority of water softener manufacturers offer metered control valves. Most units also allow you to change how much reagent is used for each regeneration. To reduce the environmental effect of water softeners and save reagent usage, both of these actions are advised. The pH of the regeneration waste is lowered when acid is used for regeneration.
The effluent flow from the regeneration process can be highly significant in industrial-scale water softening plants. The calcium and magnesium salts may precipitate out as a hardness scale on the inside of the discharge pipe under specific circumstances, such as when the effluent is released in admixture with household sewage.
The same exchange process occurs when potassium chloride is used, but potassium is traded for calcium, magnesium, and iron rather than sodium. This is a more costly option that might not be appropriate for those following a potassium-restricted diet.


 

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