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NAMS 2002 Workshop - ICOM 2008

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which can adsorb on the surface of the membrane and reduce water flow. In a<br />

typical RO plant, the normalized flow may drop by 15 to 25% in the first 60 days<br />

of operation. In subsequent months, though, the decline may only be a few<br />

percent. Cleaning can often recover a good portion of this loss. Detailed<br />

operating data will be shown to examine this.<br />

Although much progress has been made in controlling fouling, further research is<br />

needed to understand and minimize this fouling. This paper will present some<br />

detailed studies of membranes analyzed during the initial 30 days of operation<br />

and characterize the organic material which leads to membrane fouling. It will<br />

also evaluate common foulants found in commercial systems that can degrade<br />

membrane performance.<br />

High rejection of contaminants is the key to the use of RO processes. The<br />

membrane which is selected must produce water that meets the water quality<br />

targets. Depending on the use of the water, these targets can vary significantly.<br />

For applications such as those in Singapore where the water is primarily used in<br />

the wafer fabrication industry, it is critical to have low concentrations of organics,<br />

as well as hardness and other salts. These very strict limits cannot be met by all<br />

membranes. Typically, high rejection, low pressure composite polyamide<br />

membranes, such as the Hydranautics ESPA2 membrane, have found much<br />

use, since they give adequate rejection and operate at the lowest possible<br />

pressure.<br />

A recent survey of commercial plants shows that hardness ions are very highly<br />

rejected, with rejections ranging from 99.88 to 99.99%. Similar rejection would be<br />

seen for most ionized metals such as iron or manganese. Likewise the divalent,<br />

negatively charged sulfate molecule has similar rejection rates. Monovalent ions<br />

such, as sodium and chloride, have much lower rejection rates, in the range of 99<br />

to 99.3%, and nitrate, which has a smaller hydrated radius, is the lowest rejected<br />

anion, at about 94-97% rejection. These rejection rates are still much higher than<br />

the values seen for brackish water treatment. Rejection of TOC is mostly in the<br />

range of 99.6 to 99.7%. This is important for places such as Singapore, where<br />

the permeate must contain less than 100 ppb of TOC. It is apparent, that these<br />

membranes can easily achieve such values for a feed stream containing 10-15<br />

ppm of TOC. From recent plant data, a detailed analysis of the rejection of<br />

various compounds will be presented, and how these are meeting the recent<br />

stringent demands of the end user.

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