Page 201 - Photodetection and Measurement - Maximizing Performance in Optical Systems
P. 201

Contamination and Industrial Systems

            194   Chapter Nine




                                             Absorbing
                                             biofilm

                                         a
                         Source            } 1    P
                         S 1                       11

                                        }  a 2  Two beams see
                                             similar film thicknesses
                        Domed
                        window                 P 12


                        Figure 9.3 Domed windows can equalize the absorb-
                        ing film atternuations, but at the risk of greater
                        speed of contamination growth.


                        if the deposited films vary on a scale much finer than source and detector, then
                        the compensation should also be effective. The real problems arise where the
                        fouling is structured at just the wrong scale. We could say that the density of
                        fouling variations with spatial frequencies of the order of the reciprocal of
                        source/detector dimensions should be low to obtain good compensation. Stated
                        less pretentiously, dirty blobs about the same size as source or detector (Fig.
                        9.4a) are bad news! They cause the attenuation to be different for the straight-
                        through (P ii) and cross (P ij) beams. One help is to make the sources and detec-
                        tors much larger than the typical blob size (Fig. 9.4b). In pumped-sample on-line
                        instruments with small cells, the options for this are rather limited. However,
                        where a four-beam attenuation measurement system is to be immersed in the
                        large scale flowing water stream typical of a water treatment works, size is
                        hardly a consideration. There is plenty of space and sample available. It there-
                        fore seems surprising that no one, to my knowledge, manufactures instruments
                        with sources the size of car headlamps, and solar-cell detectors almost as large.
                        Lamps made up from dozens of light emitting diodes are becoming common for
                        illumination and display applications, which would be ideal for such a large-
                        format turbidity or optical absorption instrument. They could still be modu-
                        lated at high speed for synchronous detection, and are likely to provide much
                        more robust measurements, both in the face of severe contamination build-up
                        and with nonuniform samples such as raw sewage and effluents.
                          The basic four-beam configuration of Fig. 9.1 is probably about right for many
                        applications, aided by optoelectronic components chosen with regard to the
                        structure of the fouling layers expected, and especially if helped by occasional
                        automatic cleaning. Although perfection is unlikely, some form of fouling com-
                        pensation using multibeam referencing with plane windows should be designed
                        in to all but the most basic instrument.


                   Downloaded from Digital Engineering Library @ McGraw-Hill (www.digitalengineeringlibrary.com)
                              Copyright © 2004 The McGraw-Hill Companies. All rights reserved.
                               Any use is subject to the Terms of Use as given at the website.
   196   197   198   199   200   201   202   203   204   205   206