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Surface Contamination. Proceedings of a Symposium Held at Gatlinburg, Tennessee, June 1964 PDF

397 Pages·1967·13.12 MB·English
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Preview Surface Contamination. Proceedings of a Symposium Held at Gatlinburg, Tennessee, June 1964

SURFACE CONTAMINATION Proceedings of a Symposium held at Gatlinburg Tennessee June 1964 Edited by B. R. FISH SYMPOSIUM PUBLICATIONS DIVISION PERGAMON PRESS OXFORD · LONDON · EDINBURGH · NEW YORK TORONTO · SYDNEY · PARIS · BRAUNSCHWEIG Pergamon Press Ltd., Headington Hill Hall, Oxford 4 & 5 Fitzroy Square, London W.l Pergamon Press (Scotland) Ltd., 2 & 3 Teviot Place, Edinburgh 1 Pergamon Press Inc., 44-01 21st Street, Long Island City, New York 11101 Pergamon of Canada, Ltd., 6 Adelaide Street East, Toronto, Ontario Pergamon Press (Aust.) Pty. Ltd., 20-22 Margaret Street, Sydney, New South Wales Pergamon Press S.A.R.L., 24 rue des Écoles, Paris 5 e Vieweg & Sohn GmbH, Burgplatz 1, Braunschweig Copyright © 1967 Pergamon Press Ltd. First edition 1967 Library of Congress Catalog Card No. 66-17932 Printed in Great Britain by Bell & Bain Ltd., Glasgow, Scotland. (2880/67) PREFACE RECOGNITION of the potential hazard presented water, and other general environmental pollu- by noxious contaminants on surfaces is by no tion. Each of the contaminants discussed in the means new. Writing in 1890, Prudden(1) Symposium has its own peculiar properties and described measurements made in hospital wards associated problems, and probably a separate showing a definite relationship between person- international meeting could be justified for each, nel movement, sweeping, etc., on airborne independent of the other. However, there are bacteria. Prudden's remark concerning skeptics basic similarities in the needs for fundamental is still applicable and is quoted as follows. research on the dynamics of contamination control, and there are close parallels in the Many usually very reasonable persons, when brought problems of establishing and administering face to face with such disagreeable facts—are disposed to petulantly exclaim that they and their friends have contamination control programs. It was the got along very well thus far with the dust which they purpose of the meeting to bring together have encountered and that they don't want to be administrative and technical persons in order to worried with the possibilities of danger which may lurk unseen about them. exchange information on surface contamination control and to identify areas requiring future Much later on, in the medical literature of the research emphasis. 1930's, a typical comment regarding the signifi- Four sessions of the Symposium were devoted cance of bacterial contamination on surfaces to fundamental research and development in the said, in substance, that there are many more fields of aerosol physics, surfaces, adhesion- strong opinions on the subject than there are redispersion, and transport-deposition. Other results of research upon which to base any administrative and technical problems were opinion. Unfortunately, these statements remain discussed in sessions on radioactive surface substantially true today. contamination control criteria, measurement The first International Symposium on Surface techniques, environmental control of surface Contamination was convened in recognition of contamination, dissemination of airborne micro- the increasing importance of contamination in organisms, radioactive contamination control regard to the health and safety of man as well applications, biological and chemical surface as the integrity of his scientific and technical contamination, insurance and economics, and machinery and products which must meet the decontamination. A review of the papers exacting requirements of the space age. In scope, presented shows a clear need for more intense the meeting covered broad areas of interest study in each of the areas covered. Especially related to redispersible and evaporable con- lacking, but which it is hoped may be forth- tamination, including radioactive, biological, coming in some future meeting, was the report chemical, and abrasive contaminants; however, of any significant results pertaining to surface the subjects were confined primarily to con- design, selection and pretreatment to control tamination of limited areas such as in a room the deposition and redispersion of contaminants. or other semi-isolated environments and did The aid and encouragement of the session not include the very important subjects of air, chairmen in conducting the meeting and their valuable comments in informal panel discussions (1) T. MITCHELL PRUDDEN, M.D., Dust and Its Dangers, are appreciated and are gratefully acknowledged. G. P. Putnam's Sons, New York (1905). ix χ PREFACE Session chairmen were : Mr. Lawrence B. Hall, National Aeronautics Dr. C. N. Davies, London School of Hygiene and Space Administration (Biological and and Tropical Medicine (Aerosol Physics). Chemical Contamination). Dr. Sydney Ross, Rensselaer Polytechnic Mr. R. G. McAllister, Liberty Mutual Institute (Surfaces). Insurance Company (Insurance and Econ- Dr. Morton Corn, University of Pittsburgh omics of Surface Contamination). (Adhesion-Redispersion). Mr. P. Cerre, Service de Contrôle des Radia- Dr. S. K. Friedlander, California Institute of tions et de Génie Radioactif, C.E.A., Technology (Transport-Deposition). Saclay (Decontamination). Mr. H. J. Dunster, UKAEA-Harwell (Control The Symposium was sponsored jointly by the Criteria for Radioactive Surface Con- American Association for Contamination Con- tamination). trol, the Health Physics Society and the Oak Mr. J. R. Prince, Oregon State University Ridge National Laboratory. These organi- (Measurement Techniques). zations helped to disseminate information con- Dr. J. L. Anderson, Space Research, Inc., cerning the Symposium and various individual Orlando, Fla. (Environmental Control of members made valuable contributions in time Contamination). and effort toward the conduct of the meeting. Prof. T. W. Kethley, Georgia Institute of Technology (Dissemination of Airborne BIRNEY R. FISH Microorganisms). Oak Ridge, Tennessee Mr. E. D. Graham, Argonne National (1966) Laboratory (Radioactive Contamination Control Applications). AEROSOL PROPERTIES RELATED TO SURFACE CONTAMINATION C. Ν. DAVIES London School of Hygiene and Tropical Medicine, London, W.C.I, England 1. DEPOSITION MECHANISMS be adjusted back to that of the aerosol, averaged over a long time, by multiplying each size group The deposition of aerosol particles on the by the reciprocal of the square of the Stokes' surfaces of a room can be effected in a number of diameter, for sizes down to 1μ at unit density, different ways, apart from their inertia giving or to ρ~*μ, for density p. This is a valuable and them a "stop-distance" along which they can be little used technique for gauging airborne and projected to encounter a surface. Inertia deposi- surface contamination; allowance should be tion is associated with moving air; only relatively made for the difference between the Stokes' and calm air, in enclosed spaces, will be considered the observed diameters (DAVIES, 1962, 1964). here. It is not possible to classify deposition 3. BROWNIAN MOTION mechanisms as belonging to the particle or to the surface; mutual action is often involved. In addition to rate of fall, a property unique Even gravity does not exclusively act on the to the particle is its Brownian motion. Assuming particle since it may initiate convection of air and that no forces exist between the aerosol particles, influence deposition by other processes than and that each has the same average kinetic settlement. energy as a molecule of air, the mean square displacement of a particle in any direction during 2. SEDIMENTATION DUE TO GRAVITY time, t is 9 In terms of weight of material, sedimentation due to gravity is the most important deposition process. It should not be disregarded as an index of aerial contamination. Horizontal pipes and where \kT is the average kinetic energy in that ducts, of circular section, invariably carry on the direction and Zndr\\F is the resistance to move- upper surface a deposit graded according to the ment at unit velocity, including the Cunningham cosine of the angle of inclination. The rate of slip factor, F. fall of the particles is proportional to their The mean square displacement is very small, density and to the square of their Stokes' as Table 1 shows; the last column gives the root diameter, for sizes from lμ to 30μ at unit density. mean square displacement, due to Brownian The air in most rooms is in random convective motion, in one day. Only those particles which movement, as is evidenced by the uniformity of are within this distance of a surface will have a deposit on upwards facing surfaces; similar chance of reaching it in one day. Considering size-distributions are obtained from samples of that a horizontal surface collects, in one day, deposits at different levels, under these circum- even particles as small as l μ diameter from a stances, and the observed size-distribution can height of 300 cm, by settlement under gravity, it ι 2 C. Ν. DAVIES will be appreciated that Brownian deposition side possess a higher average velocity than those is negligible for sizes above ΟΌΙμ diameter when coming from the cool side. The particle velocity the air is at rest. is proportional to the temperature gradient and to the reciprocal of the pressure of the gas; it is Table 1. independent of particle size. For particles exceeding ΙΌμ diameter the • Particle diameter, d Pit thermophoresis velocity is also independent of their size but in ordinary air it is only about a 0 001 μ 1-02.10" ^m^sec 94 cm/day quarter as fast as the figure for very small 001 105.10- 3 9-5 particles. The velocity is approximately 0Ό7 01 1-36.10-5 108 cm/sec for a temperature gradient of 100°C/cm; 10 5-5 .10"7 0-22 this is about the same as the rate of fall of a 5μ diameter particle. Thermal deposition can there- fore considerably exceed sedimentation in the 4. GAS DIFFUSION PROCESSES OF DEPOSITION presence of quite modest temperature gradients Gaseous diffusion is enormously faster than and is overwhelmingly the most important particle diffusion due to Brownian motion, by the mechanism for the deposition of sub-micron order of the square root of the ratio of the weight particles. of the particle to the weight of the gas molecule, Between ΙΌμ and 0Ό3μ diameter the velocity a factor of 104 to 106. Gaseous self-diffusion increases. No theoretical treatment of this range goes on continuously with no net effect upon of sizes, comparable with the mean free path of suspended particles because it is the same in all the gas molecules, has been attempted but a directions. If, however, circumstances impose a number of experimental observations have been gradient of molecular velocity or molecular made. weight upon the space occupied by the gas, The motion of particles smaller than the mean directional forces are set in action upon sus- free path of gas molecules (about 0·07μ in pended particles; they are of a kinetic or fluid ordinary air) is adequately accounted for by mechanical character according as the particles theory but there are difficulties in interpreting are small or large in relation to the mean free experimental data for large particles. These do path of the gas molecules. The resulting particle not respond to the differences in the impacts of movements can be very much more rapid than gas molecules coming from hot and cold regions particle diffusion and play a significant part in because they are too heavy. A radiometric surface contamination. force is produced, however, if the particle is a good enough insulator to acquire a temperature 5. THERMOPHORESIS gradient along its surface in the same direction Gradients of gas-molecular velocity arise from as that in the gas. temperature differences which may be imposed A tangential gas flow is set up, towards the on the gas by the enclosing surfaces or may hotter region, with the maximum velocity originate in the particles by their absorbing distant one mean free path from the particle radiation. Thermal deposition may result when surface. The reaction on the particle drives it the temperature gradient is imposed externally down the temperature gradient (FUCHS, 1964). and causes thermophoresis of aerosol particles. Difficulties arise because the particles of high For a particle smaller than about 0-03μ thermal conductivity are found experimentally diameter, in air at one atmosphere, movement in to move nearly as fast as thermal insulators; a gradient of temperature results because the this is 20-40 times faster than theory indicates. molecules of gas which strike it from the warm The reason appears to be the neglect of the AEROSOL PROPERTIES 3 distortion of the original distribution of gas- similar effects to the gradient of molecular molecular velocities which is caused by the velocity, resulting from temperature difference, presence of the particles. Allowance for this has but may be isothermal. recently been made by DERYAGUIN and BAKANOV At least two gases must be present and a (1962). concentration gradient is necessary; gas diffusion A recent observation, so far unexplained proceeds along this direction and small particles theoretically, is that particles from 6μ down to are impelled in the direction of the diffusion 1·5μ diameter, which move at a constant flow of the heavier gas by differential molec- velocity in still air, show a rise in thermophoretic ular bombardment; this is diffusiophoresis velocity with decreasing size when the thermal (WALDMANN, 1959). motion takes place at right angles to a stream of Particles which are large compared with the aerosol (DAVIES, 1964). mean free path experience a fluid-mechanical Each of these departures from theory is in the force due to Stefan flow. This is a bulk gas direction of enhanced deposition. movement which preserves constant pressure when the components of a mixture of gases 6. PHOTOPHORESE; diffuse at unequal rates (DERYAGUIN and DUKHIN, 1956). When the temperature gradient results from Imagine a vapour, not necessarily of higher the absorption of radiation by a particle the molecular weight than air, which is condensing phenomenon is termed photophoresis. If the upon a surface below the dew point temperature. particle absorbs light and is a thermal insulator Gaseous diffusion is essentially a process of it becomes heated on the side which receives interpénétration; hence air molecules diffuse radiation, warms the adjacent gas and moves away from the surface as vapour molecules away from the source of radiation by one of the diffuse towards it. The vapour molecules are two mechanisms described for thermophoresis. condensed at the surface, so there is no build-up The resulting force is considerably greater than of vapour, but neither is there a source of air at radiation pressure. the surface. Hence a drift of vapour-air mixture Complicated situations arise with transparent towards the surface is established, to avoid the and selectively absorbing particles which may creation of a pressure deficiency, and constitutes become hotter on the side remote from the the Stefan flow which exerts a hydrodynamic source of radiation and move towards it; drag on aerosol particles and impels them magnetic particles may execute a helical motion towards a surface upon which vapour is condens- (ROHATSCHEK, 1956). ing. Conversely they are repelled away from an Although no specific instances of the deposi- evaporating surface which is surrounded by a tion of particles being occasioned by solar dust-free space resembling that around a hot radiation have ever been cited, there is little object. doubt that it is an appreciable factor, particu- The effect can be estimated numerically from larly since the force acts continuously and is the equation of DERYAGUIN and DUKHIN (1956). independent of the distance from the surface. For water condensing on a cold wall it produces It is a possible mechanism for the transport of a deposition velocity for aerosol particles of the cosmic dust into the troposphere. order of magnitude of the rate of fall of 1μ diameter particles; the effect is therefore 7. DIFFUSIOPHORESIS AND STEFAN FLOW unlikely to be large, but, under certain circum- The other way in which gas diffusion can stances, aerosol particles could be encouraged induce a motion of particles is in the presence of to deposit on cold surfaces in a room by Stefan a gradient of molecular weight. This produces flow. 4 C. N. DAVIES 8. ELECTRICAL DEPOSITION Deposition due to a cloud of similarly charged particles expanding by mutual repulsion is Aerosol particles will move in a uniform unaffected by air movements since a uniform electric field only if they are charged; in a non- concentration is obtained at all points at any uniform field, however, they become induced instant. The total rate of deposition on the dipoles and move towards the stronger field containing walls is approximately intensity unless the original charge on a particle is large enough to impose an initial direction of dn/dt = -4nn2q2F/3^d motion. where n is the number of particles per cm3 and q The particles of an aerosol which carried a is the charge per particle in electrostatic units. unipolar charge repel one another so that the The general theory has been worked out by cloud expands and the particles deposit on the PICH (1962). surfaces enclosing it. Using the above simple formula, the rate of The velocity of a particle carrying a charge of deposition of aerosols carrying 10 electrons per q electrostatic units in a field of 1 V/cm is particle has been calculated. The results are shown in Table 3 as the aerosol concentration, u = qF/900 πηα in number of particles per cm3, which is necessary Table 2. to result in deposition on the enclosing walls of 1/10 of the aerosol per hour. Electrical mobility Particle diameter, d (q = 4-8.10"10 e.s.u.) Table 3. 0-001/* 20 cm/sec (V/cm) 001 21.10-2 Concentration needed to cause 01 2-7.10-4 1/10 of the particles to deposit in 10 1-1.10-5 Particle diameter, d one hour 100 9-4.10-7 ΟΟΟΙμ 0 08 particles/cm3 001 7-5 01 570 In Table 2 the electrical mobility, or velocity 10 14,600 in a field of 1 V/cm when carrying a charge of 1 electron (4-8. 10"10 e.s.u.) is given for The table shows that appreciable wall loss due particles of various sizes. The table shows that to homopolar charging occurs for sizes up to deposition velocities exceeding 1 cm/sec (which 01 μ or more and that the rate is very large corresponds to the settlement of 15-20μ dia- for ultrafine aerosols. For a charge of only one meter particles) are available for particles electron per particle the last column needs below 01 μ diameter, even if they carry a multiplying by 100. charge of only a few electrons, in fields of 1000 V/cm or less. As long as the particles have a FOSTER (1959) has performed experiments upon the deposition of homopolar smokes. slight charge, very fine sizes are quickly removed When the charges are of the same sign but differ by moderate electric fields; above 0·1μ really in magnitude the expansion of the cloud is powerful fields and large charges on the particles decreased by the induction of dipoles in the more are necessary. Plastic surfaces are often very weakly charged particles. good insulators and hold static charges for a long time, but only in exceptional circumstances is contamination by particles greater than 9. CONCLUSIONS 01 μ diameter likely to result from adventitious It is difficult to see what other aerosol electrical deposition. properties could be associated with the deposition AEROSOL PROPERTIES 5 of surface contamination in enclosed spaces; the account of their high mobility due to the loss or the retention of contamination is not an Cunningham slip factor. The question then arises aerosol property and is considered by other as to how small a particle has to be for its authors in this symposium, as is the influence thermal energy to cause it to evaporate from a of the nature of the surface. surface soon after deposition. The deliberate enhancement of the rate of The work of CORN (1961) suggests that deposition by working on the aerosol with particles of 50μ diameter adhere to a dry surface acoustic radiation, or some other means, also with a force of the order of 01 dyne. The seems irrelevant to the accidental contamination molecular attractive force can then be taken as which has been the subject of this paper. about 0Ό02</ dynes and the work of removal as μ Summarizing the findings we conclude: 0·002</. IO"8 ergs. μ (i) Gravitational deposition is very effective The thermal energy is of the order of for particles down to about 1μ, unit 3fcT/2«4. 10"14 ergs. The critical particle size density spheres. below which spontaneous evaporation might be (ii) Brownian motion is negligible for sizes expected is thus over 0-01 μ. ά = 4 . 10" 14/2 . 10" 11 «0 002/1 (iii) Thermophoresis is very important for μ sizes below 5μ and is the main mechanism This is getting down to aggregates of compara- around 01 μ. tively few molecules. It seems as though mole- (iv) Photophoresis could be important in the cular adhesion can be relied upon to overcome presence of sunlight over a similar range the tendency towards thermal evaporation as of sizes. long as the concept "particle" is thermo- (v) Diffusiophoresis and Stefan flow are dynamically valid. unlikely to be major factors but could cause a rather slow precipitation of aerosol particles along with moisture REFERENCES condensing on cold surfaces. CORN, M.,J. Air Poll Contr. Assoc. 11, 523, 1961. (vi) In the presence of static charge on DAVIES, C. N., Nature, 195 (4843), 768, 1962; lb. 201 surfaces, electrical deposition of particles (4922), 905, 1964; Recent Advances in Aerosol Re- below 0·1μ is increasingly rapid as the size search. Pergamon Press, Oxford, 1964. DERYAGUIN, Β. V. and BAKANOV, S. P., Dokl. Acad. decreases. Very strong fields would be Nauk SSSR. 147, 139. Nature 196, 669, 1962. needed for larger particles. Homopolar DERYAGUIN, Β. V. and DUKHIN, S., Dokl. Acad. Nauk aerosols can deposit by mutual repulsion SSSR. Ill, 613, 1956. of the particles at a high rate for ultrafine FOSTER, W. W„ Brit. J. Appi. Physics. 10 (5), 206, 1959. aerosols. Above 0·5μ, however, the effect FUCHS, Ν. Α., The Mechanics of Aerosols. Eni. edn. Pergamon Press, Oxford, 1964. is small unless the charging is high. PICH, J., Staub. 22 (1), 15, 1962. It is worth noting that, apart from gravity, ROHATSCHEK, H., Acta Phys. Austriaca. 10 (3), 227, 267, the processess considered tend to favour the 1956. deposition of very fine particles; this is on WALDMANN, L., Zeits. Naturforsch. 14a (7), 589, 1959. LIGHT SCATTERING INSTRUMENTATION FOR COUNTING AND SIZING PARTICLES CARL V. SEGELSTROM, Jr. Royco Instruments, Inc., Menlo Park, California 1. INTRODUCTION window illuminates it. While an individual Counting and sizing of particulate matter has particle of cigarette smoke is too small to be been accomplished for many years by manual detected by the unaided eye, when light strikes techniques. That is, particles are collected by billions of them relatively close together the any one of several techniques and then either a resultant scattered light is readily observed. total or statistical count is made through a Photometric devices utilizing this principle have microscope using a graduated reticule to deter- been in use for many years. These devices, while mine size. As individual components of manu- useful for relating one environment to another factured precision equipment have become or for comparisons of environmental changes smaller and smaller and clearances between with time, do not provide size information or a moving surfaces have decreased, the require- numerical count. To accomplish this it is neces- ments placed on measuring techniques and sary to thin out or dilute the concentration so equipment have increased. Occasionally it that the particles may be examined one at a time. becomes necessary to increase the counting Obviously where the concentration of particles frequency to provide a continuous count; in is low, such as in a well designed and maintained some cases 100 per cent of the gas or liquid must clean room, dilution would not be necessary. be examined, such as the gas in gas bearing The Royco Particle Counter operates on the gyros. The atmosphere in clean fabrication and principle of right angle light scattering (Fig. 1). assembly areas must be monitored at frequent Energy from a well regulated white light source intervals. Small particle sizes must be measured, of high intensity is collected in a pair of lenses at times below the reliable limits of manual and focused on a 1 mm χ 2 mm aperture in a techniques. In certain situations it is necessary to shim stock knife edge. A pair of projection know immediately when contamination levels lenses, in turn, focuses the energy onto an exceed preset limits. For these and other illuminated volume 1x2x2 mm which is en- reasons, it was necessary to evolve better closed by a black body. The light source used is a techniques for counting and sizing particulate G.E. 2331 lamp which is operated at a filament matter. The light scattering technique provides a temperature of about 2850°K. This produces useful and accepted tool to meet this need. a good white light and also results in about 400 hr bulb life. Care has been taken in the lens 2. COUNTING AND SIZING AIRBORNE system to minimize random rays of light PARTICLES traveling down the barrel and causing excessive A. The light scattering technique stray light in the viewing area. Stray light in the We have all observed cigarette smoke in a still viewing area must be minimized since a high room on a sunny afternoon where the smoke level of background light will produce a high settles in layers and the sun streaming in a noise output at the photomultiplier thereby Β

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