Table Of ContentSURFACE  CONTAMINATION 
Proceedings of a Symposium held at 
Gatlinburg Tennessee 
June 1964 
Edited  by 
B. R. FISH 
SYMPOSIUM PUBLICATIONS DIVISION 
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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 
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