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Membrane and Desalination Technologies - TCE Moodle Website

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158 N.K. Shammas <strong>and</strong> L.K. Wang<br />

monodispersed in solution might constitute a conservative surrogate for Cryptosporidium that<br />

would not require direct verification.<br />

3. Molecular markers: The suitability of molecular markers as surrogates for Cryptosporidium should<br />

be considered on a case-by-case basis. While the justification for using microorganisms <strong>and</strong> inert<br />

particles as surrogates for Cryptosporidium is more straightforward given that all are particulates,<br />

molecular markers are dissolved substances that are fundamentally different from particulate<br />

contaminants. As such, the removal mechanisms for molecular markers may be different than for<br />

those associated with discrete particles in many cases. However, semipermeable membranes that<br />

are capable of achieving very high removal efficiencies for dissolved substances may be capable of<br />

achieving similar removal of particulates such as Cryptosporidium. In addition, porous membranes<br />

with very fine pore sizes may be able to remove large macromolecules via mechanisms similar to<br />

those that filter discrete particles. Thus, the use of molecular challenge particulates is permitted for<br />

the purposes of challenge testing under the LT2ESWTR if the molecular marker used is determined<br />

to be conservative for Cryptosporidium <strong>and</strong> is discretely quantifiable.<br />

A variety of molecular markers have been historically used to characterize the pore size or<br />

removal capabilities of membrane processes. For example, macromolecular protein compounds<br />

are used to determine the molecular weight cut-off (MWCO) for many UF membranes.<br />

In addition, fluorescent dyes such as Rhodamine WT <strong>and</strong> FDC Red #40 are used to<br />

characterize NF <strong>and</strong> RO membranes. These substances have high spectrophotometric absorbance<br />

characteristics that allow measurement <strong>and</strong> detection at the mg/L level (29). However,<br />

these low molecular weight ( 500 Da) solutions could only be used with RO <strong>and</strong> less<br />

permeable NF membranes. If molecular markers are considered for challenge testing, it is<br />

desirable to use compounds that are more similar to discrete particles such as macromolecular<br />

proteins. It is also recommended that a mass balance be conducted on the feed, filtrate, <strong>and</strong><br />

concentrate streams prior to challenge testing, to assess the efficacy of using a particular<br />

molecular marker.<br />

With some molecular markers, it may be difficult to demonstrate removal in excess of 3 log<br />

unless sufficiently sensitive instrumentation is used. For challenge tests conducted with<br />

molecular markers, the feed <strong>and</strong> filtrate concentrations are typically quantified in terms of<br />

mass per unit volume. If the analytical method is specific for the molecular marker used in the<br />

test, use of a mass-based concentration is acceptable since the mass of a known substance can<br />

be related to moles, which is a discrete quantification. As is the case with any challenge<br />

particulate, gross measurements cannot be used for the purpose of quantification. This<br />

requirement would preclude the use of analytical techniques such as TOC monitoring <strong>and</strong><br />

conductivity monitoring in most cases (3).<br />

4.8. Challenge Test Solutions<br />

Generation of an appropriate challenge test solution is an essential component of an<br />

effective test program. The purpose of the challenge test solution is to deliver the challenge<br />

particulate to the module of interest under the established test conditions. The design of the<br />

challenge test solution includes:<br />

1. Establishing acceptable water quality of the solution.<br />

2. Determining volume requirements.

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