Document Xzn0pbK66m9jQnXGoneomwNQR
FILE NAM E: No Safe Threshold (NST)
DATE: 1962 Jan-Feb DOC#: NST008
DOCUM ENT DESCRIPTION: Trade Journal Article - A Toxicologist's View of Threshold Lim its
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NLM014699926
AMERI CAN
IK
Industrial Hygiene
ASSOCIATION
VO LU M E 23, NUM BER I January-February, 1962
American Industrial Hygiene Conference Park-Sheraton Hotel, Washington, D. C .
May 13-17, 1962
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A ME R I C A N
\il Hygitiene A S S O C I A T I O N Journal
Volume 23
.
January-February, 1962
Number I
TABLE OF CONTENTS
C h a n g in g O b j e c t iv e s in O c c u p a t io n a l H e a l t h ......................................................................... 1
, Theodore Hatch
N e w C o n c e p t s a n d F u t u r e T r e n d s in T o x ic o l o g y ................................................................. 8
Herbert E. Stokinger
M o d e r n C o n c e p t s o f A ir S a m p l in g a n d P r o b l e m s f o r t h e F u t u r e ........................... 20
H. F. Schulte
M odern C o n c e pt o f A nalytical C h e m ist r y in I n d u str ia l H ygiene and P r o b l e m s f o r t h e F u t u r e ................................. ................................................................................... 26
/. Cholak .
M odern C o n c e pt s o f D ia g n o sis and T r ea tm en t in O ccu pa tio n a l M ed ic in e........ 30
Mitchell R. Zavon, M.D.
A T o x ic o l o g is t 's V ie w o f T h r e s h o l d L im it s .............................................................................. 37
Henry F. Smyth, Jr., Ph.D.
T h r e s h o l d L im it s and M axim al A cceptable C o n c e n t r a t io n s : T h e ir D e f in i t io n a n d I n t e r p r e t a t io n , 1 9 6 1 ......................................... ................................................................. 45
. Herbert E. Stokinger, Ph.D., Chairman, Threshold Limits Committee, American Conference of Governmental Industrial Hygienists
A n I mproved C o n tin u o u s I ntern a l-E lectrolysis A nalyzer for G aseou s F l u o r id e s in I n d u s t r ia l E n v ir o n m e n t s .............................................. ...................................... 4 8
O. H. Howard, A.B., and C. W. Weber, Ph.D.
S e p a r a t io n a n d A n a l y s is o f D u s t in L u n g T i s s u e ........................................................ ........ 58
N. A. Talvitie and Lial W. Brewer
I n -S e r v ic e S o l v e n t C l e a n in g o f E l e c t r ic M o t o r s ................................................................. 62
D. L. Stoddard and W. R. Wells
D u s t C o n t r o l in t h e A s b e s t o s T e x t il e I n d u s t r y ................................................................. 67
Benjamin F. Postman, M.E.
U s e o f St a t is t ic a l M e t h o d o l o g y in E n v ir o n m e n t a l M o n it o r in g ............................. 75
Gerald W. Kerr
P l a n n in g V e n t il a t io n f o r N u c l e a r R e a c to r F a c il it ie s ....................................................... 83
Bruce J. Held
A Sy st em For E x po su r e o f M ice to an A t m o s p h e r e C o n ta in in g C arbon P a r t ic l e s .........................................................................:.............................................................................. 88
Eric G. Comstock, Roger R. Rue, and J. H. Gast
N e w s o f L o c a l S e c t io n s ............................................................................................................................. 91
Pr e s id e n t 's Pa g e ....................................................................................... ..................................................... A -2
American I ndustrial H ygiene A ssociation J ournal, published bi-monthly by the American Industrial Hygiene
Association. Dohrman H . Byers, Editor; Kenneth W. Nelson, Associate Editor; Philip Drinker, Consulting Editor.
Editorial offices, 1014 Broadway, Cincinnati 2, Ohio. George D. Clayton, Publications Manager. Business office,
14125 Prvost, Detroit 27, Michigan. The subscription price is $7.50 per year in U.S.A.; $7.75 in Canada; $8.25
elsewhere. Single copies, when available, may be purchased from the business office, $1.50 per copy in .S.A.;
$1.75 elsewhere. Copyright 1962, by the American Industrial Hygiene Association. Entered as second class
matter at the post office at St. Paul, Minnesota. The Association reserves the right to edit all advertisements and
to refuse advertising copy when it does not meet the high standards adopted by the Association. Library of
Congress Catalogue No. 57-3191.
'
Printed for the American Industrial Hygiene Association by
THE BRUCE PUBLISHING COMPANY, SAINT PAUL 14, IvlINNESOTA
inuary-February, 1962
tment in occupational d remarkably in recent mtals of diagnosis and ally changed at all. As ices, it carries occupat, yet this specialty has to contribute in the ves its special problems, affect such a large prolfully employed adult
becoming more conand comparatively less imical change. We are c in our diagnostic techleously depending more ithods to indicate the >f effect. Diagnosis and lecialty have advanced :ss we can train pracogical terms, future ad i and starts rather than
:ont.
1/ASSer, and H. L. Jaffr: Blood Healthy Aged 65 to 106 Years. ? Med. 94: 463 (1957); M aster, .nd H. H . M a r k s: The Normal and Its Clinical Implications. 143:. 1464 (1950) . . O sol (E ditors): New Gould Oraw Hill Book Company, Inc.,
M. Sc h u m a n : `'Silo-Filler's Caused by Nitrogen Dioxide.
162: 153 (1956). H. J ones, and J. R. Brow n. After Exposure to an Ester of \cid. / . Amer. Med. Assoc. 171:
io n : A case of supposed organic , with permanent neurological
ity. Scientific American 183: 44
lie Present Evolution of Man.
3: 206 (Sept. 1960).
.
nger, and J. P hIa ir: Radiation
treasing Clinical Significance of es of Body Fluids. A nn. inf.
id Cholinesterase Activity. AM A
403 (1957). m m . F. M yers, C. S heba, and latological Survey of Industrial ic-Deficient Erythrocytes. AM A
510 (1959).
. ..
A . G ilm a n : The Pharmacological
2nd Ed. The Macmillan Co.,
ir a k i: PAM (Pyridine-2-Aldoxime for Alkyl Phosphate Poisoning.
166: 1834 (1958).
A Toxicologist's View of Threshold Limits
HENRY F.SMYTH, JR., Ph.D. Mellon Institute, 4400 Fifth Avenue, Pittsburgh, Pennsylvania
JH Conformance with a threshold limit may lead to more absorption of vapor than oes conformance with a numerically identical maximal acceptable concentration, because the former is a time-weighted average concentration, while the latter is a limit below which all measurements should fall. The adverse effects which threshold limits are expected to guard against may not include cortical reflexes. Whether or not such reflex effects are of any importance to the well-being of the industrial worker is not completely clear.
I AM on record1 as concluding that experi mental study of the effects of repeated inhalation by animals has been as sound a basis for setting threshold limits as any other basis which has been used for the values of the American Conference of Governmental Industrial Hygienists (AC G IH ). A consider able proportion of the values set on any basis has been modified later as experience has accumulated, and the proportion has been no greater for those based on experimental toxicology than for other bases. It is the collection of experience through industrial hygienists and industrial physicians, with annual reconsideration of values, which has made the threshold limits lists dependable.
However, some details are suggested by toxicological considerations. All that I have to say is related to the paragraph which has been used for several years as part of the foreword to the annual tables of threshold limits issued by the American Conference of Governmental Industrial Hygienists.2 I quote:
a normal workday. The amount by which these figures may be exceeded for short periods without injury to health depends upon a number of factors, such as the nature of the contaminant, whether very high concentrations even for short periods produce acute poisoning, whether the effects are cumulative, the frequency with which high concentrations occur, and the duration of such periods. All must be taken into consideration in arriving at a decision as to whether a hazardous situa tion exists. Special consideration should be given to the application of these values in the evaluation of the health hazards which may be associated with exposure to combinations of two or more substances."
I shall discuss points suggested by three
phrases from the quoted paragraph:
"The time-weighted average concentra
tion," "The amount by which these figures may
be exceeded," and "Without adverse effect,"
"Threshold limits should be used as guides in the control of health hazards and should not be regarded as fine lines be tween safe and dangerous concentrations. They represent conditions under which it is believed that nearly all workers may be repeatedly exposed day after day, without adverse effect. The values listed refer to time-weighted average concentrations for
This paper was presented at the Tenth Annual Conference of the Pennsylvania Department of Health, University Park, Pennsylvania, on August 23, 1961.
and follow with a brief summary of our own exploration of the conditioned reflex, which leads out of my discussion of the third phase.
"Time-Weighted Average Concentrations"
The Maximal Acceptable Concentrations (MAC's) of the American Standards Associa tion Z-37 Committee, are authoritative opinions, which are not widely referred -to.
In the mid 1950's the Z-37 Committee
37
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January-February, 1962
undertook to review and to revise earlier standards which it had issued, and to extend the rather brief list to include additional industrial materials. This large Committee, operating under the awkward rule of con sensus, with some members unable to vote until official action of their societies has in structed them, has made less than moderate progress. Since 1957 four standards have been issued, Carbon Tetrachloride,3 Ben zene,4 Toluene5 and Xylene.6 The numerical values of these MAG's are identical with the 1960 Threshold Limits Values of the ACGIH, namely 25, 25, 200, and 200 parts per million by volume (ppm) respectively.2
The agreement is much less than one would think from the correspondence of the numerical values. This is an illustration of the weakness of quoting numbers divorced from their context. The threshold limit values refer to time-weighted average con centration for a normal work day, as ex plained in the paragraph I quoted.
which the standards guard, and of the toxico
logical mechanisms which cause these in.
juries. I made a special study of this subject
in 1956/ and concluded that the injuries
guarded against varied widely. I urged that
some clue to the type of injury be included
in tabulations of standards. Injuries are ex
plicitly described in ASA Standards and in
American Industrial Hygiene Association
Hygienic Guides, but not in any tabulations
I have seen published. Indeed, ASA has set
the precedent of naming two standards for
inhalation of one substance, to guard against
two kinds of injury. In effect, the Xylene
Standard5 says, "To guard against discomfort
to workmen, keep concentrations below 50
ppm, and to guard against narcosis and ,
anemia, keep concentrations below 200 ppm." I
My 1956 paper7 concluded that the 238 |
ACGIH threshold limits and tentative 1
threshold limits then extant guarded against |
nine different adverse effects.
I
On the other hand, the maximal accept able concentrations of the Z-37 Committee refer to that concentration which should not be exceeded at any time during a normal work day. MAC's are peak concentrations, not averages. The Carbon Tetrachloride standard reads 25 ppm, "with the under
1. Twelve per cent guarded against acute systemic toxicity. With these, the total amount absorbed in one day usually deter mines whether injury results, and the timeweighted average concentration is an appro priate guide to sate, working conditions. Among the exceptions may be the cyanides,
standing that variations should fluctuate around 10 ppm."3 If this standard is followed
whose detoxication in the body is so rapid that the average during a briefer period, or
literally, the time-weighted average will be even the instantaneous peak, is more im in the neighborhood of 10 ppm, only 40% portant.
of the threshold limit. The Xylene standard reads 200 ppm, "with the understanding that variations in concentration should fluctuate below this level."5 Here again, a person working in the MAC conceivably could ab sorb about half as much as if he were working in the threshold limit concentration.
Thus the numerical identity of the stand ards of MAC and TL for four vapors, actually mean that the Z-37 Committee con cludes that the exposures of workmen should be considerably less than those which the ACGIH Committee concludes are unlikely to cause adverse effect.
2. Thirty-three per cent guarded against chronic, toxicity. With these, the total amount absorbed during several days or even weeks determines whether injury results, and the time-weighted average concentration is an appropriate guide to safety.
3. Twenty-three per cent guarded against narcosis. The degree of narcosis in a subject varies with the concentration in the fluid bathing certain cells in the central nervous . system, and this is quickly responsive to the concentration being inhaled. The timeweighted average concentration is useless to judge safety. The concentration being
The question of which concept is sound, breathed should never exceed some particular
average, or maximum, requires some con value, regardless of the day's average.
sideration of the type of injuries against
of is 4. Twenty-six per cent guarded against
fit (i I
'uard3 and of the toxieo- J*
which cause these in -
ial study of this subject 1
uded that the injuries 1
d widely. I urged that i
5 of injury be included
dards. Injuries are ex-
A.SA Standards and in
Hygiene Association
not in any tabulations
. Indeed, ASA has set
ling two standards for I
tance, to guard against 1
In effect, the Xylene 1
lard against discomfort |
ncentrations below 50 |
against narcosis and 1
itions below 200 ppm." 1
ncluded that the 238 I
imits and tentative 1
xtant guarded against 1
effects.
1
,, .
1
guarded against acute jf
th these, the total 1
ne day usually deter- 1
esults, and the time- |f
mtration is an appro- j|
working conditions. g
may be the cyanides, |
the body is so rapid |f
1 a briefer period, or |
peak, is more im- |
:ent guarded against ,f
h these, the "total 3
several days or even
er injury results, and
Jge concentration is j.?
safety.
p
sent guarded against j
narcosis in a subject ;
tration in the fluid I
the central nervous
:ly responsive to the |
haled. The time- I
itration is useless to |
concentration being j|
:eed some particular |
lay's average.
I
nt guarded against I
uncomfortable but not harmful irritation of the eye, nose, or throat. Clearly, for these, the instantaneous concentration is useful for guarding comfort; the daily average is not useful; and neither has much bearing on
safety. 5. Six standards are for asphyxiants, but
these threshold limits are standards of good practice, so far below a truly injurious con centration that there is no need to debate which form of standard is the more sound.
6. Three standards guarded against fume fever. The total amount in the lung at any one time is the significant quantity. Lung clearance seems to proceed so quickly that the average concentration in an hour is more significant than that in a day, and a standard based on a maximum in the air seems a sounder index of safety.
7. Two standards guarded against eye pigmentation, more a cosmetic defect than an interference with vision. This condition develops slowly over a very long period, and the time-weighted average seems a sound control.
8.. Two standards guarded against allergic sensitization. With these it is possible that no concentration can be set to which some previously sensitized person will not react. Hence, the standards could well be a form of zero, the smallest amount which can be analytically estimated. The nature of the most sensitive practical analytical method should determine which form of standard is the better.
9. One standard guarded against cancer.
We know so little about the causation of
cancer by most substances that it may be
prudent to limit the concentration to a form
of zero, the smallest amount which can be
analytically estimated. The nature of the
most sensitive practical analytical method
should determine which form of standard is
better.
For fifty per cent of the substances listed in
1956, I found that the ASA Maximal
Acceptable Concentration concept of an in
stantaneous or peak concentration was the
sounder protection against' adverse effect,
while the ACGIH Threshold Limit concept
of a maximum time-weighted-average con
centration over one working day was ade quate protection in forty-six per cent of the standards. Since an excessive time-weighted average is impossible if a well-chosen maxi mum instantaneous concentration is never exceeded, I see no need for the concept of an average to protect health. However, I recognize that the requirements of many sampling and analtyical methods make it more practical to determine conformance with an average over an appreciable period than to determine conformance with a maximum. Developments in analytical in strumentation are reducing the relative con venience of a standard for average concentra tions, and in some instances make the average very cumbersome to determine.
In summary, when Z-37 and ACGIH standards for inhalation are numerically identical, conformance with the Z-37 stand ard results in absorption of less toxicant than does conformance with the ACGIH standard. For about half the substances listed the ACGIH concept is physiologically wrong. The Z-37 concept, while likewise physio logically wrong for half the substances in the ACGIH list, errs on the side of safety. Health would be more consistently protected if all standards were written in terms of maximum peak concentration during a working day, rather than in terms of the time-weighted average throughout the day.
"The Amount by Which These Figures May Be Exceeded"
The ACGIH Committee contemplates that some operations will be conducted in con centrations above the threshold limit for brief periods, for they devote an entire sentence to suggesting the pertinent factors to be con sidered. Many industrial hygienists are quali fied to interpret these pertinent factors for specific substances. Many others, including even lawyers, may blindly rely upon the threshold limits as averages of exposures to unlimited peak concentrations, and this reliance may result in harm to those exposed. How can the Threshold Limits Committee better guard against such misinterpretation?
It seems to be practically impossible to
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] anuary-February, 1962
conduct some industrial operations without exposing workmen to concentrations above the threshold limit. When the particular sub stance has a threshold limit which guards against acute toxicity, such as that for arsine, workmen may be seriously injured by rela tively brief peak exposures. The operation should be fully automated, or if a workman must be present, adequate personal protection must be provided, maintained, and con sistently used. When the substance has a threshold limit which guards against eye, nose, and throat irritation and is far below an injurious concentration, such as acetalde hyde, exposures well above the threshold limit can have no effect except to produce complaints from workmen, and some work men will perceive no discomfort.
It ought to be possible to agree upon the penalty to health which may be exacted if a threshold limit is exceeded, even continually, and to indicate this in tabulations, as a guide to the solution of problems where operations under the limit are impractical. It is very difficult to find this information in the litera ture, partly because the bases for threshold limit values have not been explicitly stated by the AGGIH Committee until very recently.
"Without Adverse Effect"
The threshold limits values are stated to be guides to conditions under which it is be lieved that nearly all workers may be re peatedly exposed without adverse effects, and they are not fine lines between safe and dan gerous conditions. Hence most industrial hy gienists do not lose faith in the soundness of the values when they learn that every year a few are changed, usually downwards, as a re sult of industrial experience which comes to the attention of the Committee. However, serious uncertainty was evoked several years ago when it was rumored that values enforced in Russia are in some instances one-tenth or less of the ACGIH values. It was obvious that such a difference could be due only to a difference in concept of what the values should accomplish, because it is thoroughly demonstrated in American industry that guidance by the ACGIH values results in safe working conditions. Nevertheless, lack of in formation fostered doubts.
In this country the Russian values for con centrations of contaminants in the working environment first became generally known and debated following the X II International Congress on Occupational Health in Helsinki in 1957. The paper by Smeljansky8 was par ticularly noteworthy, stating that the concen trations considered safe, and enforced in Rus sian industry, are lower than in the United States for a number of vapors. The basis for the values was stated to be experimental studies using the Pavlov conditioned reflex technique.
Elkins9 has recently compared the values used in Russia and in the United States, grouping the substances by nature of action, chemical structure, or physical form. In some categories he finds agreement to be good, in others the Russian values are slightly lower than ours, in still others they are one-tenth or less of ours. He states that where agree ment is least, the Russian values are said to be based on conditioned reflex studies with animals.
It is now possible to scrutinize the details
of the bases for some of the Russian values,
and to infer something of the philosophy
under which they have been set, through
the translations by B. S. Levine, made avail
able by a Public Health Service Research
Grant
13,14,15,16
The experimental methods which form the bases for the few values I shall discuss, are described in Book 3, pages 102-128, which is the third (1957) report of the U.S.S.R. Com mittee on the Determination of Limits of Al lowable Concentrations of Atmospheric Pol lutants.12 This Committee deals with atmos pheres outside of work places, but the meth ods it describes seem to be the same as those relied upon for industrial exposures.
Apparently only six experimental methods are employed. Odor and mucous membrane (eyelid) irritation is a considerably refined method for an estimate of the aggressive characteristics of substances. Less accurate estimates of these characteristics have been much relied upon for setting ACGIH thres hold limits.7 The Russian method uses ten human subjects, analytically verified concen trations, and several days working time for
Industrial] ICD
each substaf fied with "objectionali tration, as i i concentraticjg from pure is used for
The othe| thesis that sv the sympathl the cerebral^ tions can hi phenomena jg the substance^
The pneui the thesis thl self against 1 when they Sympathetic 1 bral cortex tion by causi volume, and i cuff over theI human subjeel utes inhalatioj stance, then tration which! tion is the thr| in setting star ject is conscic inhaled.
The plethysl the same thesis flex here is al striction, detecj of a finger.
The optical;) the thesis that. ters, even whf cause a sympatj lying nearby elapsed time isl a second, betwl human eyelid, luminosity. Im lL , reduces this time. S for training three I. tests of chronaxy re periods of inhalatio: tions, to determine tl tration.
Aavasn
] anuary-February, 1962
Russian values for conninants in the working xame generally known g the X II International ional Health in Helsinki 1 by Smeljansky8 was par- I stating that the concen- I fe, and enforced in Rus- g ver than in the United 1 of vapors. The basis for | ed to be experimental | .vlov conditioned reflex j
I ly compared the val,ues ig
in the United States, ces by nature of action, j physical form. In some / jreement to be good, in alues are slightly lower f hers they are one-tenth | states that where agreeissian values are said to >ned reflex studies with
to scrutinize the details | ; of the Russian values, ling of the philosophy | lave been set, through | . S.. Levine, made avail- g ealth Service Research
nethods which form the
lues I shall discuss, are
pages 102-128, which is
irt of the U.S.S.R. Com-
lination of Limits of Al- :
ns of Atmospheric Pol- :
nittee deals with atmos- ;
-k places, but the meth-
to be the same as those
trial exposures.
.
x experimental methods and mucous membrane a considerably refined j nate of the aggressive istances. Less accurate ^ laracteristics have been j r setting ACGIH thresussian method uses ten ytically verified concen- | days working time for i
Industrial Hygiene Journal
41
each substance. The Russians are not satis fied with the subjective evaluation of the "objectionable" characteristics of a concen tration, as is done in this country. The lowest concentration which can be distinguished from pure air by any one of the ten subjects is used for setting a standard.
The other five methods depend on the thesis that substances have an initial effect on the sympathetic nervous system, producing in the cerebral cortex reflex processes whose ac tions can be most sensitively detected by phenomena not part of the direct action of the substance.
The pneumographic method depends on the thesis that the body tends to defend it self against objectionable substances, even when they are not consciously perceived. Sympathetic reflexes mediated by the cere bral cortex respond to odor and nasal irrita tion by causing changes' in respiratory rate, volume, and rhythm. By means of a rubber cuff over the thorax, the respiration of a few human subjects is followed during a few min utes inhalation of a concentration of a sub stance, then of pure air. The lowest concen tration which produces a difference in respira tion is the threshold of effect to be considered in setting standards, whether or not the sub ject is conscious that the substance is being inhaled.
The plethysmographic method depends on the same thesis of a defense reflex. The re flex here is a change in blood vessel con striction, detected by changes in the volume of a finger.
The optical chronaxy method depends on the thesis that irritation of the olfactory cen ters, even when not consciously perceived, cause a sympathetic irritation in optic centers lying nearby in the cerebral cortex. The elapsed time is measured, in thousandths of a second, between electrical stimulation of a human eyelid, and perception of an illusion of luminosity. Irritation from inhaled material reduces this time. Several days are required for training three human subjects, and for tests of chronaxy resulting from five-minute periods of inhalation of various concentra tions, to determine the least effective concen tration.
The adaptometric test depends on the same thesis of irritation of the optic center, sym pathetic to irritation of the olfactory center. It measures the sensitivity to light of trained human subjects, when breathing vapors for fifteen-minute periods after an hour of adap tation of the eye to darkness. The eye is more sensitive when a vapor is being inhaled, whether or not the subject is aware of the inhalation.
The sixth test is the conditioned reflex de termination in rats. It is the only one which is designed to produce chronic toxic effects. It seems to depend on the thesis that activa tion of any sympathetic reflex decreases the ability of the cerebral cortex to carry out con ditioned reflex actions. It requires several weeks for training. Rats are trained to reach for food as a reflex response to a bell and to a colored light, but to avoid reaching when a buzzer sounds. By a complex scheduling of these events, one classifies the central nervous activity of the trained rats as to strong and weak, balanced and unbalanced, and uses some of each type in each experimental group. The trained rats are subjected to six months of daily inhalations of a substance. Every day their reflexes are tested, recording the time lapse between the signal and the learned response. At the end of six months one can judge which of the concentrations tested resulted in no change in reflexes, and which produced minimum changes. Some rats are sacrificed at once for tissue study, others are kept for thirty days to judge re covery of their reflex behavior, then tissues are studied. The entire study on one sub stance requires almost a year.
By relying upon the results of these six tests, the Russians indicate their belief that people should not be subjected to inhalation of a substance at a concentration which re sults in any detectable physiological response. They may feel that if there is such a re sponse, a lifetime of exposure may result in injury, impairment of function, disability. I have seen no evidence that experience in in dustry plays any part in setting their stand ards. Our feeling has been that people should not be subjected to inhalation which they find consciously objectionable, or which is likely to lead to disability or suffering. Since
42
.
January-February, 1962
the concepts of what the standards are ex
pected to guard against are so widely dif
ferent, it should not be surprising that values
for specific substances may be widely dif
ferent. Experience under standards based
upon our concept, during almost twenty
years, gives us confidence that we are pro
tecting health.
A review of some of the few available pub
lications of Russian experimental work may
be informative. In 1956 Novikov published
the experimental work on benzene, upon
which the Russian standard seems to be
based (Reference 14, p. 185). He considers
that the blood-cell changes we see from ben
zene may be secondary effects of sympathetic
disturbances in that part of the central
nervous system which regulates the hemo
poietic system. He appears to believe that
disturbances in the central nervous system
which he detects by behavioral changes in
conditioned rats, parallel the disturbances
which affect the hemopoietic system, and that
the only way to prevent blood-cell changes
is to keep concentrations too low to affect be
havior. At 20 ppm benzene he finds changes
in conditioned reflex behavior, most marked
in rats of weak, and of unbalanced strong,
higher nervous activity.' At. 4 ppm he finds
no effect. Those who have utilized his re
sults seem to feel that there is no difference
between human and rat sensitivity to this
central nervous system effect, for Elkins9 re
ports that the Russian MAG for benzene is
6 ppm. This is to be compared with the
AGGIH figure of 25 ppm,2 based on long
industrial experience.7
In 1957 Borisova published experimental
work on dichloroethane, upon which the
Russian standard seems to be based (Refer
ence 15, p. 110). Using humans, he found
that the threshold for increased sensitivity to
light, respiratory changes, and constriction of
capillaries was 1.5 ppm, below the odor thres
hold, while 1.0 ppm had none of these effects.
Elkins9 reports that the Russian MAC for
dichloroethane is 2.5 ppm. This is to be com
pared with the AGGIH figure of 100 ppm,2
based on animal experiment, human experi
ence, and analogy with carbon tetrachloride,
but not revised to allow for more recent views
about the latter substance.7
In 1958 Melekhina published the experi mental work on formaldehyde, upon which the Russian standard seems to be based (Reference 15, p. 135). Using humans, the time to perceive a sensation of light as a re sult of electrical stimulation of the eyelid, was reduced by 0.07 ppm formaldehyde, and not affected by 0.03 ppm, while the threshold of odor was 0.06 ppm. Elkins9 reports that the Russian MAC for formaldehyde is 0.08 ppm. This is to be compared with the AGGIH figure of 5 ppm,2 based on com plaints of workmen in industry.7
Our Exploration of Conditioned Reflex
About eighteen months ago, my group set out to explore the utility of the conditioned reflex technique, with much less knowledge of the Russian methods than we now have. A manuscript describing our first results is in press,17 and a research grant for further work in methodology has been authorized by the National Institutes of Health (OH-16).
There are American reports of one middleaged woman18 and two young adult males19 who worked for several weeks in noticeably high, but unmeasured concentrations of mixed vapors containing the monomethyl ether of ethylene glycol (methyl cellosolve solvent). The three were incapacitated, with headache, drowsiness, forgetfulness, and dis orientation, diagnosed as "toxic encephalo pathy," and attributed to inhalation of methyl cellosolve. The workers returned to normal after a few weeks of rest in a hospital, with out other therapy. A survey of one establish ment using the same mixed solvent in the same way, found eight of nineteen workers with non-disabling symptoms suggesting the same injury.20 Because of these observations, several attempts were made to produce such symptoms in animals.21'22'23 The symptoms were not found, but no specialized behavioral techniques were used at that time.
This recorded experience suggested methyl cellosolve as a useful substance for explora tory studies of the utility of the conditioned reflex technique. We asked ourselves if such symptoms in over-exposed humans would have been predicted had behavioral studies been understood and applied before methyl
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muary-February, 1962
published the experi aldehyde, upon which . seems to be based ). Using humans, the sation of light as a reulation of the eyelid, pm formaldehyde, and >m, while the threshold l. Elkins9 reports that ' formaldehyde is 0.08 ; compared with the ppm,2 based on coml industry.7
Conditioned Reflex
nths ago, my group set ility of the conditioned i much less knowledge is than we now have. A ; our first results is in i grant for further work aeen authorized by the Health (OH-16), l reports of one middlevo young adult males19 ral weeks in noticeably red concentrations of ining the monomethyl ycol (methyl cellosolve vere incapacitated, with , forgetfulness, and disd as "toxic encephalo1 to inhalation of methyl :ers returned to normal rest in a hospital, withsurvey of one establishe mixed solvent in the jht of nineteen workers ymptoms suggesting the ^se of these observations, 2 made to produce such s.2i,22,23 The symptoms no specialized behavioral 1 at that time. erience suggested methyl 1 substance for exploraitility of the conditioned 2 asked ourselves if such ;xposed humans would [ had behavioral studies i applied before methyl
;V.
Industrial Hygiene Journal
43
cellosolve was first used industrially, and if the threshold limit would be lower than it now is.
With no knowledge of the Russian meth ods, we trained rats in a conditioned avoid ance response. At the sound of a buzzer, they climbed a pole, because originally they had received an electric shock while standing on the floor when the buzzer sounded.
Inhalation of methyl cellosolve for four hours daily for several days reduced the num ber of rats which climbed the pole when they heard the buzzer, but up to a lethal concen tration all rats were able to climb when given the electric shock. Inhalation of the vapors reduced the effect of conditioning, but left them able to climb to escape pain. The num ber of rats affected increased with the days of inhalation, but seemed to reach a maxi mum by fourteen days. The effect seemed minimal at 125 ppm, five times the ACGIH threshold limit.2 Some rats, allowed to rest for fourteen days without inhalation, re turned to the conditioned behavior without retraining.
Contrasted with the behavior of methyl cellosolve, ethyl alcohol produced no such be havioral change short of a concentration which caused frank depression and ataxia.
This exploratory work, by conditioned re flex methods possibly less sensitive than the Russian methods, does not show an effective concentration lower than the current ACGIH threshold limit, with a vapor to which has been attributed transient human disability arising in the central nervous system.
Summary
Experience in this country with threshold limits based upon toxicological experiment with animals has been good.
Despite the fact that the limits are used only as guides, and are not sharp lines sepa rating safe from injurious atmospheres, more consideration should be given to the condi tion the numbers are meant to represent. In particular the time-weighted average concen tration is physiologically wrong for about half of the limits, and can result in injurious ex posures. If the threshold limits referred to a maximum concentration existing at any time
during the working day, the substances for which this is physiologically wrong, would be controlled by a conservative standard.
Tables of threshold limits would be more useful if they indicated the injury which could result from a small excess, in order to guide the management of exposures where full conformance is impossible.
The philosophy of the Russian maximum allowable concentrations seems to be that workmen should not be exposed to any con centration which produces a detectable physi ological response, with no consideration as to whether such a response is harmful.
An exploratory study of the conditioned re flex behavioral technique indicates that the method may detect effects which other toxic ological methods do not suggest.
References
1. Sm y th , H. F. Jr.: The Toxicological Basis of Threshold Limit Values. I. Experience with Threshold Limit Values Based on Animal Data. Amer. Ind. Hyg. Assoc. J. 20: 341 (Oct. 1959).
2. ACGIH: Threshold Limit Values for 1960. AM A Arch, of Envir. Health. 1: 140 (Aug. 1960).
3. ASA: American Standard Maximum Acceptable Conccntration of Carbon Tetrachloride. Amer. Stds. Assoc., New York (Jan. 15, 1957).
4. ASA: American Standard Maximal Acceptable Concen tration of Benzene. Amer. Stds. Assoc., New York (Oct. 28, 1960).
5. ASA: American Standard Maximal Acceptable Concen tration of Toluene. Amer. Stds. Assoc., New York (Oct. 28, 1960).
6. ASA: American Standard Maximal Acceptable Concen tration of Xylene. Amer. Stds. Assoc., New York (Oct. 28, 1960).
7. Sm y th , H. F., J r.: Improved Communication--Hygienic Standards for Daily Inhalation. Amer. Ind. Hyg. Assoc. Quart. 17: 129 (June 1956).
8. Sm el ja n sk y , S. B.: Hygienische Begrndung der nor mativvorschriften Bezglich maximal-zulssiger Konzen trationen toxischer Stoffe in der Luft der Betriebsrume. Proceedings of the X II International Congress on Occupational Health, Vol. I l l , p. 80, Helsinki (1957).
9. E l k in s , H. B.: Maximum Allowable Concentrations, A Comparison in Russia and the United States. AMA Arch. Envir. Health.2: 45 (Jan. 1961).
10. Limits of Allowable Concentrations of Atmospheric Pollutants, Book 1, 1952. V. A. Ryazanov, Editor, B. S. Levine, Translator. U. S. Department of Commerce, Office of Technical Services, Washington 25, D. C.
(59-21173).
11. Limits of Allowable Concentrations of Atmospheric Pollutants, Book 2, 1955. V. A. Ryazanov, Editor, B. S. Levine, Translator. U. S. Department of Commerce, Office of Technical Services, Washington 25, D. C. (59-21174).
12. Limits of Allowable Concentrations of Atmospheric Pollutants, Book 3, 1957. V. A. Ryazanov, Editor, B. S. Levine, Translator. U. S. Department of Commerce, Office of Technical Services, Washington 25, D. C. (59-21175).
13. U.S.S.R. Literature on Air Pollution and Related Occupational Diseases. Vol. 1, Jan. 1960. B. S. Levine, U. S. Department of Commerce, Office of Technical Services, Washington 25, D. C. (60-21049).
14. U.S.S.R. Literature on Air Pollution and Related Occupational Diseases. Vol. 2, Mar. 1960. B. S. Levine, U. S. Department of Commerce, Office of Technical Services, Washington 25, D. C. (60-21188).
53' 'V''
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. 15. U .S.S.R. Literature on A ir Pollution and Related Occupational Diseases. Vol. 3, May 1960. B. S. Levine, U. S. Department of Commerce, Office of Technical Services, Washington 25, D. C. (60-21475).
16. U .S.S.R. Literature on A ir Pollution and Related Occupational Diseases. Vol. 4, Aug. 1960. B. S. Levine, TJ. S. Department of Commerce, Office of Technical Services, Washington 25, D. C. (60-21913).
17. G oldberg, M . E ., C. C . H a u n , and H . F . Sm y t h , J r .: Toxicological Implication of Altered Behavior In duced jby an Industrial Vapor. Toxicol, and Applied Pharmcttol. In Press.
18. D onley, D. E .: Toxic Encephalopathy and Volatile Solvents in Industry. Report of a Case. J. Ind. Hyg. Toxicol. 18: 571 (1936).
19. P a r so n s, C. E., and M. E. M . P arso n s: Toxic Ence phalopathy and "Granulopenac Anemia" Due to
January-February, 2962
Volatile Solvents in Industry. Report of Two Cases
J. Ind. Hyg. Toxicol. 20: 124 (1938).
*
20. G reenberg, L . , M. R . M ayers, L. J. G oldwater, ty. I J. B urk e, and S. M o s k o w it z : H ealth Hazards in th I Manufacture of ``Fused Collars." I. Exposure to ! Ethylene Glycol Monomethyl Ether. / . Ind. Hyp : Toxicol. 20: 134 (1938).
21. W erner, H . W., C. Z. N aw rock i, J. L. M itchell .
J. W. M iller, and W. F. von O e tt in g en : Effects of
Repeated Exposures of Rats to Vapors of Monalkyl |
Ethylene Glycol Ethers. }. Ind. Hyg. Toxicol. 25: 374 j
(Oct. 1943).
J
22. Walther, R .: Toxicology of the Glycols. Arch. Gewer- bepath. Gewerbehyg. 11: 326 (1942).
23. Sm y th , H . F., J r., and C. P . C arpenter, Mellon Institute: Unpublished.
Occupational Health Training
The Public Health Service, through its Division of Occupational Health, will conduct a series of four related courses April 23-May 18, 1962, at the Occupational Health Research and Training Facility, Cincinnati, Ohio. In dustrial Hygiene Engineering, designed for industrial hygienists and engineers in the field of occupational health, and Industrial Hygiene Chemistry, for chemists and chemical engineers in this field, are given concurrently, April 23May 4. Trainees in both courses meet together for the first week for instruction in industrial hygiene and medicine, toxicology, and principles pertaining to evaluation of the environment. Meeting separately the second week, work for the hygienists covers temperature and humidity measurements, illumination, noise measurement and control, and industrial ventilation; for the chemists, laboratory analyses for lead, free silica, and solvents ; and spectroscopy, polarography, x-ray diffraction, electron microscopy, and gas chromatography. Much time in both courses is spent in the laboratory.
A related course for the industrial hygienists and engineers, Heat Stress and Its Control, May 7-11 (1 week), covers methods of measurement and control of industrial exposure to extreme physiological stress caused by temperature and humidity, with attention also on associated personnel problems. Course time is divided about equally between lectures and laboratory exercises.
A related course for the chemists and chemical engineers is Solvent Analysis Techniques, May 7-18 (2 weeks). Lectures and laboratory exercises cover distilling column fractionation and gas chromatographic separation of the components in binary and complex solvent mixtures, in the principles and application of simple physical and chemical tests, and in ultraviolet and infra red spectrophotometric procedures for identification and determination of separate components.
Full descriptions of these courses are given in the Training Program Bulletin which is available on request. Trainees may register in single or related courses. Applications or requests for information should be addressed to the Chief, Training Program, Robert A. Taft Sanitary Engineering Center, 4676 Colum bia Parkway, Cincinnati 26, Ohio, or to a PHS Regional Office.
p E R lf T aril America dustrialj mendiril This is| large nU of indc there ciples t | tion, interprd
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