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Membrane and Desalination Technologies - TCE Moodle Website

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Treatment of Food Industry Foods <strong>and</strong> Wastes by <strong>Membrane</strong> Filtration 247<br />

Table 6.3<br />

Typical recoveries, trans-membrane pressures, power requirements, consumption, <strong>and</strong><br />

resulting energy costs based on applied pressures with an overall motor/pump efficiency<br />

of 40%. Assumed energy cost 0.05 US$/kWh<br />

Recovery (%) Pressure (kPa) Consumption (kWh/day) Energy cost (US$/m 3 )<br />

MF 90–98 100 77.5–70.8 0.004–0.0035<br />

UF 90–98 300 231.5–212.5 0.012–0.011<br />

NF 75–95 500 463.5–365.5 0.023–0.018<br />

RO 50–80 1000 1389–868.3 0.070–0.043<br />

3. OPERATIONAL PROBLEMS AND ENGINEERING SOLUTIONS<br />

All aspects of fouling involve the trapping of some type of material within the membrane<br />

process device itself or on the surface of the membrane. Since the causes, symptoms, <strong>and</strong><br />

cures are different, the following five types of fouling are discussed below (23, 24):<br />

1. <strong>Membrane</strong> scaling<br />

2. Metal oxides fouling<br />

3. Colloidal fouling<br />

4. Biological fouling<br />

5. Cleaning agent fouling<br />

The problems of membrane scaling <strong>and</strong> metal oxides fouling are common to all membrane<br />

systems, regardless of the type or source of feed water stream (i.e., sea water or food<br />

processing water). Colloidal <strong>and</strong> biological types of fouling are specifically important in<br />

the design of a membrane system for treating food processing water <strong>and</strong> wastewater. To<br />

establish the optimal membrane cleaning regime, it behooves the operator to underst<strong>and</strong><br />

clearly the nature <strong>and</strong> the extent of the interaction of cleaning agents with the membrane.<br />

3.1. <strong>Membrane</strong> Scaling<br />

Precipitation of dissolved salts results from exceeding the solubility limits in a concentrated<br />

stream. This may occur because the salts in feed water are normally concentrated from<br />

two to four times. This is a function of system recovery; 50% results in a concentration of<br />

2 <strong>and</strong> 75% results in a concentration of 4. The most common precipitates encountered are<br />

those of calcium carbonate, calcium sulfate, <strong>and</strong> silica. Calcium carbonate precipitation can<br />

be prevented by lowering the feed pH by the addition of hydrochloric acid. Carbonates <strong>and</strong><br />

bicarbonates are then converted to carbon dioxide gas that passes through the membrane<br />

without difficulty. The precipitation of calcium sulfate can be retarded by the addition of a<br />

sequestering agent, such as sodium hexametaphosphate. The silica precipitation can be<br />

prevented by reducing system recovery to keep silica concentrations below saturation.

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