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Membrane and Desalination Technologies - TCE Moodle Website

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<strong>Desalination</strong> of Seawater by Thermal Distillation <strong>and</strong> Electrodialysis <strong>Technologies</strong> 553<br />

high-pressure pumps in RO process, which produce noise during operations. Various technological<br />

measures can be utilized to reduce noise levels so that the risk to the operators can be<br />

minimized (26). The operations should be kept away from population centers.<br />

The more important form of emission from desalination that raises environmental concerns<br />

comprises the discharge of concentrated saltwater after the desalination process is completed<br />

(27). The TDS of wastewater from a conventional DWTP is approximately 3–5 times higher<br />

than that in the feed; the flow rate is 20–50% of feed flow. The waste also contains chemicals<br />

used in the pretreatment of feed water, such as antiscalants, surfactants, <strong>and</strong> acid.<br />

Major disposal alternatives for the water pollution are given in Table 12.4. Each method<br />

varies in complexity <strong>and</strong> costs. Sewer discharge is commonly the least complex <strong>and</strong> least<br />

Table 12.4<br />

List of disposal alternatives for water pollution in DWTP<br />

Technology Brief description<br />

Ocean disposal Ocean disposal is typically done several miles offshore with diffusers.<br />

Dilution by seawater can reduce the contents of the waste. The<br />

treatment plant outfall location may be affected by water quality rules<br />

Discharge to sewer <strong>and</strong><br />

surface waters<br />

<strong>and</strong> regulation.<br />

Sewer discharge is the simplest; however, it depends on the ability of the<br />

wastewater treatment plant to accept high salinity discharge. Surface<br />

water discharge involves discharge to a point of outfall such as tidal<br />

lake or brackish canal. Dilution by surface waters can reduce the<br />

contents of wastes. The location of discharge <strong>and</strong> the pretreatment<br />

requirement are determined by state <strong>and</strong> regulatory agencies; water<br />

quality testing (e.g. bioassay toxicity) is required.<br />

L<strong>and</strong> application Irrigation is sometimes used for the waste streams with relatively lower<br />

salinity. Saline tolerant vegetation <strong>and</strong> habitat are required. This is<br />

usually determined by site-specific soil <strong>and</strong> drainage characteristics<br />

Evaporation pond Desalting concentrate is discharged to ponds <strong>and</strong> evaporated to dryness<br />

for final disposal. It is l<strong>and</strong> intensive <strong>and</strong> requires relatively dry<br />

climates. Dry salt is the final waste product, which must be<br />

characterized <strong>and</strong> disposed of accordingly as solid waste. This is<br />

generally applicable only in arid environments <strong>and</strong> then usually in an<br />

inl<strong>and</strong> location<br />

Deep well injection In deep well injection, the waste streams are injected to the ground <strong>and</strong><br />

are permanently stored in the injection zone. It is very commonly used<br />

Zero discharge <strong>and</strong><br />

industrial reuse<br />

by the desalination water treatment plants<br />

Zero discharge of wastes can be achieved by thermal processes, which<br />

greatly reduce or eliminate the waste stream. The thermal processes are<br />

energy intensive <strong>and</strong> very costly. Wastes must be characterized <strong>and</strong><br />

disposed of accordingly. Marketable salts for general industrial uses<br />

can be recovered. This is still in the development stages, but past<br />

attempts indicate that recovery of marketable byproducts is<br />

economically difficult

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