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Membrane and Desalination Technologies - TCE Moodle Website

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<strong>Membrane</strong> <strong>Technologies</strong> for Point-of-Use <strong>and</strong> Point-of-Entry Applications 623<br />

requirements, (c) the water pressure to meet the supply <strong>and</strong> rejection rates (this value has to be<br />

considered to determine whether the RO unit will be operated on the normal operating<br />

pressure of a home water system or using a booster pump), (d) the rejection rate or the<br />

percentage of contaminants to be removed by the membrane, <strong>and</strong> (e) the monitoring or testing<br />

method of the system’s performance. Details of the major factors in operating an RO system<br />

in POU/POE are provided below.<br />

3.5.1. Types <strong>and</strong> Initial Concentrations of the Contaminants in Feed Water<br />

Types <strong>and</strong> initial concentrations of the contaminant entering the RO process are the crucial<br />

factors that determine the quality of the purified water. Overall water quality affects the<br />

efficiency of an RO system <strong>and</strong> its ability to remove specific contaminants. In operating an<br />

RO unit, it is required that the water source entering the RO units must not contain more than<br />

10 grains of hardness (0.2 mg/L of iron <strong>and</strong> less than 0.25 mg/L of manganese). The TDS<br />

should be about 500 ppm. The higher the TDS, the greater the osmotic pressure <strong>and</strong> the lower<br />

the recovery rate of treated water (Table 14.6).<br />

Moreover, the initial concentration of contaminants is also affected depending on the<br />

rejection rate. Rejection rates need to be high enough to reduce the contaminant level in the<br />

untreated water to a safe level. For example, if the initial concentration of nitrate is relatively<br />

high as 120 mg/L, 90% of nitrate removal would still leave 10% or 12 mg/L of nitrate in<br />

the treated water. This value is greater than the maximum contaminant level (MCL), which is<br />

10 mg/L for nitrate allowed in drinking water. Thus, the rejection rate of nitrate at 10% from<br />

this RO unit is not an appropriate value for purified water. Water with very high levels of<br />

nitrates (such as 100 mg/L) would remain near or above the health st<strong>and</strong>ard levels even after<br />

treatment. However, high concentrations of nitrate levels are not expected in feed water <strong>and</strong><br />

indicate unusual problems that require special investigation <strong>and</strong> h<strong>and</strong>ling. The NSF recommends<br />

that special designs be used for RO units where the NO3 N level exceeds 40 mg/L<br />

(nitrates as used in this part refers to nitrate-nitrogen or NO3 N).<br />

3.5.2. Water Pressure <strong>and</strong> Temperature<br />

The st<strong>and</strong>ard at which manufacturers rate RO system performance is 77 F, 60 pounds per<br />

square inch (psi), <strong>and</strong> TDS at 500 ppm (30). <strong>Membrane</strong> productivity is very sensitive to<br />

changes in water temperature. As water temperature increases, water flux increases due to the<br />

higher diffusion rate of water through membrane. It is reported that the amount of treated<br />

Table 14.6<br />

Best available technologies (include RO) for radionuclides (40 CFR 141.66(g), 142.65(a))<br />

Contaminant Best available technology<br />

Combined radium-226 <strong>and</strong> radium-228 Ion exchange, reverse osmosis, lime softening<br />

Uranium Ion exchange, reverse osmosis, lime softening,<br />

coagulation/filtration<br />

Beta particle <strong>and</strong> photon radioactivity Ion exchange, reverse osmosis

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