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Membrane and Desalination Technologies - TCE Moodle Website

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564 J.P. Chen et al.<br />

polyester fabric. The support layer is very porous <strong>and</strong> hence does not reject the salt. In the<br />

following separate manufacturing step, a semipermeable membrane skin is formed on the<br />

polysulfone substrate by interfacial polymerization of monomers containing amine <strong>and</strong><br />

carboxylic acid chloride functional groups.<br />

In the 1970s, Cadotte prepared a composite membrane that consisted of a thin layer of PA<br />

formed in situ by condensation of branched polyethyleneimine <strong>and</strong> 2,4-diisocyanate on a<br />

porous polysulfone membrane (8). The effect of surface modification on the performance of<br />

an aromatic PA–TFC membrane (FT-30) has been studied (9). After soaking in solutions of<br />

various concentrations of hydrofluoric acid (HF), fluorosililic acid, <strong>and</strong> their mixtures at<br />

controlled temperature for various times, the membrane was rinsed with deionized (DI) water<br />

<strong>and</strong> tested for their RO performances. For membranes soaked in 15 wt.% HF solution for<br />

7 days, the flux increased from 3.5 to 18 L/m 2 h, whereas NaCl separation increased from<br />

94.5 to 95.3% under the same operating pressure of 250 psig. For membrane soaked in 15 wt.<br />

% HF solution for 4 days, X-ray photoelectron spectroscopy showed that the fluorine ratio on<br />

the membrane surface increased from 0 to 0.012 on the fresh membrane. The value increased<br />

to 0.044 for the membrane immersed in 15 wt.% HF solution for 75 days. Thus, surface<br />

chemical modification contributed to the dramatic increase of the flux as well as the thinning<br />

of the selective skin layer, whereas NaCl separation remained practically unchanged.<br />

The discovery of TF membranes is a breakthrough in achieving flows <strong>and</strong> rejections<br />

suitable for seawater desalination. In some cases, three-layer configurations are used for<br />

extra durability <strong>and</strong> performance. Some characteristics of the two membranes are listed in<br />

Table 13.1.<br />

Thin film composite membranes are subject to continuous development. <strong>Membrane</strong>s with<br />

chlorine resistance, low energy, <strong>and</strong> low fouling have been produced. Recently, about 60% of<br />

seawater recovery has been reported for some extra high-rejection TF membranes. RO<br />

systems were originally designed using flat CA or hollow fiber membranes that were retrofitted<br />

with TFC membranes of polyurea <strong>and</strong> PA. The TFC PA membranes have many<br />

advantages in comparison with CA or hollow fiber membranes. These include wider chemical<br />

<strong>and</strong> physical tolerance ranges, higher silt density index (SDI) tolerance, feasibility of operation<br />

at higher temperatures, <strong>and</strong> higher pH tolerance. These make pretreatment easier <strong>and</strong> less<br />

expensive, <strong>and</strong> operation easily controlled. Furthermore, the introduction of the TFC PA<br />

Table 13.1<br />

Characteristics of cellulose acetate <strong>and</strong> thin-film membranes<br />

Parameters Cellulose acetate Thin film<br />

Temperature Up to 30 C Up to 50–90 C<br />

Operating pressure (psi) Up to 450 typically; up to 800 occasionally 100–1,200<br />

pH 3.0–9.0 1.0–12.0<br />

Chlorine tolerance Fair Poor<br />

Oxidization tolerance Good Poor<br />

Rejection (%) Good Excellent

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