15 T h e R o l e of B i o l o g i c a l
Monitoring
in
Medical
and E n v i r o n m e n t a l Surveillance
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CARL B. MONROE Corporate Health and Safety, Rohm and Haas Company, Box 584, Bristol, PA 19007 Biological Monitoring is used by environmental engineers to assess the control of workplace exposures to toxicants and by medical personnel to detect medical conditions associated with exposure to these substances. Linch (1) has made an extensive review of techniques that are available for use in biological monitoring. This paper will explore the application of biological monitoring in industrial hygiene and occupational medical surveillance programs, relate biological monitoring to other occupational medical surveillance techniques, and discuss the importance of informing workers of the purpose for the tests and the practical meaning of test results. The approach to occupational health surveillance through biological monitoring is diagramed in Figure 1. Definition of Occupational Biological Monitoring Biological monitoring in occupational health surveillance consists of bioassay or other tests that are administered to workers with known or presumed exposures to potential toxicants in the workplace for the purpose of measuring body uptake of the toxicant, an index of exposure, or detecting pathophysiologic effects of the toxicant, an index of toxicity. Since exposure and toxicity are the determinants of the hazard potential of a toxic substance, the occurrence of either one of these phenomena is reason for preventive health measures. Examples of biological monitoring tests that are applied in environmental and medical surveillance programs are listed in Table I. Application of Biological Monitoring in Environmental and Medical Surveillance The multidisciplinary approach to the evaluation and solution of occupational health problems may involve the use of 0097-6156/81/0149-0223$05.00/0 © 1981 American Chemical Society
In Chemical Hazards in the Workplace; Choudhary, G.; ACS Symposium Series; American Chemical Society: Washington, DC, 1981.
C H E M I C A L HAZARDS IN T H E W O R K P L A C E
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I d e n t i f y the Problem
Confirm adequate c o n t r o l of exposure ο Measure body uptake of t o x i c a n t Confirm adequate exposure l i m i t ο Determine medical e f f e c t of exposure
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Other c o n s i d e r a t i o n s ο I n v e s t i g a t e non-occupational occurrence of t o x i c a n t
II.
Structure B i o l o g i c a l M o n i t o r i n g Program
ο
0
III.
Implement Program
Select b i o l o g i c a l monitoring t e s t Measure the t o x i c a n t o r i t s ο b i o t r a n s f o r m a t i o n products Measure a b i o l o g i c a l response 0 associated with toxicant's mechanism of a c t i o n Formal b i o l o g i c a l m o n i t o r i n g program 0 Purpose of t e s t Schedule of t e s t i n g 0 Method o f a n a l y s i s of t e s t r e s u l t s ο ( c l i n i c a l or epidemiologic) Defined outcome of t e s t r e s u l t s ο ( a l t e r work c o n d i t i o n s , medical removal, e t c * ) Information to be provided t o t e s t ο subjects
Inform worker of purpose of t e s t i n g M e d i c a l personnel conduct
tests
Test r e s u l t s t h a t show medical d i s e a s e s and d i s o r d e r s analyzed by m e d i c a l personnel - Data provided t o environmental engineer without personal i d e n t i f i e r s Test r e s u l t s t h a t show body uptake ( a n a l y s i s f o r t o x i c m a t e r i a l s and nond i s e a s e medical i n d i c e s of exposure) analyzed by environmental engineer Inform worker of t e s t outcome and meaning of t e s t r e s u l t Decide a p p r o p r i a t e course o f a c t i o n
Figure 1.
Flow diagram illustrating the use of occupational biological monitoring
In Chemical Hazards in the Workplace; Choudhary, G.; ACS Symposium Series; American Chemical Society: Washington, DC, 1981.
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MONROE
Biological
Monitoring
for
Surveillance
225
TABLE I EXAMPLES OF BIOLOGICAL MONITORING TESTS USED IN ENVIRONMENTAL AND MEDICAL SURVEILLANCE
Occupational Exposure
B i o l o g i c a l M o n i t o r i n g Test f o r Body Uptake
B i o l o g i c a l M o n i t o r i n g Test f o r Medical E f f e c t of Exposure
Pb
Blood Pb
Blood Z i n c
CholinesteraseInhibiting Pesticide
Blood L e v e l of P e s t i c i d e or B i o t r a n s f o r m a t i o n Product
Blood C h o l i n e s t e r a s e A c t i v i t y
Cd
Blood and U r i n a r y Cd
U r i n a r y Beta-2 M i c r o g l o b u l i n
D i e s e l Exhaust
E x p i r e d Air-CO
Carboxyhemoglobin measured i n blood or e x t r a p o l a t e d from e x p i r e d air-CO
Protoporphyrin
In Chemical Hazards in the Workplace; Choudhary, G.; ACS Symposium Series; American Chemical Society: Washington, DC, 1981.
C H E M I C A L HAZARDS IN T H E W O R K P L A C E
226
a s i n g l e t o o l o r c o n c e p t i n d i s s i m i l a r ways w i t h i n t h e specialty areas ( i n d u s t r i a l hygiene, medicine, etc.) r e p r e s e n t e d on t h e o c c u p a t i o n a l monitoring of a t o x i c a n t or i t s assess
the
integrity
several
h e a l t h team. Biological biotransformation products
o f work p r a c t i c e s ,
engineering
to
controls,
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and p e r s o n a l h y g i e n e c a n be u s e f u l i n e n v i r o n m e n t a l surveillance. M e d i c a l s u r v e i l l a n c e programs o f t e n incorporate b i o l o g i c a l m o n i t o r i n g t e s t s to screen f o r h y p e r s u s c e p t i b l e w o r k e r s and t o d e t e c t m e d i c a l c o n d i t i o n s i n t h e e a r l i e s t and most c u r a b l e s t a g e s . The p a r t i c u l a r i t y o f b i o l o g i c a l m o n i t o r i n g i s e v i d e n t i n t h e OSHA p r o m u l g a t i o n on e m p l o y e e a c c e s s t o e x p o s u r e and m e d i c a l r e c o r d s ( 2 ) w h i c h c a t e g o r i z e s b i o l o g i c a l m o n i t o r i n g t e s t r e s u l t s as an e x p o s u r e r e c o r d when t h e a b s o r p t i o n o f a s u b s t a n c e i s m e a s u r e d and as a m e d i c a l r e c o r d when p a t h o p h y s i o l o g i c e f f e c t s a r e d e t e r m i n e d . The r o l e o f b i o l o g i c a l m o n i t o r i n g i n e n v i r o n m e n t a l and m e d i c a l s u r v e i l l a n c e c a n be d i f f e r e n t i a t e d on t h e b a s i s o f t h e p u r p o s e and outcome o f t e s t i n g i n t h e two s i t u a t i o n s . In e n v i r o n m e n t a l s u r v e i l l a n c e , the g o a l of b i o l o g i c a l t e s t i n g is to e v a l u a t e the exposure q u a n t i t y of the h a z a r d p o t e n t i a l posed by a t o x i c s u b s t a n c e . An e n v i r o n m e n t a l s u r v e i l l a n c e p r o g r a m might i n c l u d e the r o u t i n e performance of b i o l o g i c a l t e s t s to d e t e c t body u p t a k e o f w o r k p l a c e c o n t a m i n a n t s t o c o n f i r m t h e effectiveness s u f f i c i e n t by s a m p l i n g . The manufacturing environmental
o f i n d u s t r i a l h y g i e n e p r a c t i c e s t h a t a p p e a r t o be o t h e r measurements, s u c h as a r e a o r p e r s o n a l r o u t i n e a s s e s s m e n t o f u r i n a r y cadmium i n w o r k e r s p l a s t i c s h e e t c o n t a i n i n g cadmium p i g m e n t s when measurements h a v e shown a i r b o r n e cadmium l e v e l s
t o be w e l l w i t h i n a c c e p t a b l e l i m i t s i l l u s t r a t e s t h i s t y p e o f environmental monitoring. A l t e r n a t i v e l y , environmental s u r v e i l l a n c e t h a t i s t a r g e t e d t o work s i t u a t i o n s where t h e r e i s a s i g n i f i c a n t p o t e n t i a l f o r overexposure to a t o x i c m a t e r i a l , e . g . , uranium mining o p e r a t i o n s w i t h h i g h a i r b o r n e concentrations o f u r a n i u m , c a n be e n h a n c e d c o n s i d e r a b l y by b i o l o g i c a l m o n i t o r i n g because b i o l o g i c a l a b s o r p t i o n i s probably t h e b e s t p a r a m e t e r t o show t h e e f f e c t i v e n e s s o f good p e r s o n a l h y g i e n e , h o u s e k e e p i n g , and t h e p r o p e r u s e o f r e s p i r a t o r s or p r o t e c t i v e c l o t h i n g i n t h i s t y p e o f e x p o s u r e s i t u a t i o n . The outcome o f b i o l o g i c a l m o n i t o r i n g i n e n v i r o n m e n t a l s u r v e i l l a n c e i s the d e f i n i t i o n of the e x t e n t to which a t o x i c m a t e r i a l has b e e n a b s o r b e d by t h e b o d y . When n o n - o c c u p a t i o n a l s o u r c e s o f c o n t a m i n a t i o n have been e x c l u d e d , t h i s i n f o r m a t i o n a l l o w s the e n v i r o n m e n t a l e n g i n e e r to judge whether e n v i r o n m e n t a l c o n t r o l measures are
adequate or
need
refinement.
In m e d i c a l s u r v e i l l a n c e , b i o l o g i c a l m o n i t o r i n g i s a p r e v e n t i v e m e d i c a l t o o l t h a t i s u s e d t o d i s c e r n t h e human t o x i c i t y of p o t e n t i a l t o x i c a n t s at exposure l e v e l s present i n the w o r k p l a c e . E v i d e n c e o f human t o x i c i t y c a n r e s u l t f r o m i n d i v i d u a l h y p e r s u s c e p t i b i l i t y , inadequate exposure l i m i t s which might have been d e r i v e d from a n i m a l d a t a , or u n s u s p e c t e d
In Chemical Hazards in the Workplace; Choudhary, G.; ACS Symposium Series; American Chemical Society: Washington, DC, 1981.
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15.
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Monitoring
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Surveillance
227
excursions i n workplace contamination. Medical monitoring might be done when i n d u s t r i a l hygiene measurements show that a p o t e n t i a l t o x i c a n t i s present i n the workplace at l e v e l s that are considered to be s a f e . The r o u t i n e measurement of blood c h o l i n e s t e r a s e l e v e l s among workers i n w e l l - c o n t a i n e d organophosphate p e s t i c i d e manufacturing operations i s an example. When the workplace i s contaminated w i t h a p o t e n t i a l t o x i c a n t to such an extent that a s i g n i f i c a n t p o t e n t i a l e x i s t s f o r overexposure, b i o l o g i c a l monitoring i s one medical s u r v e i l l a n c e t o o l that can be used to assure that environmental p r o t e c t i v e measures have prevented the occurrence of h e a l t h e f f e c t s . B i o l o g i c a l monitoring of blood c h o l i n e s t e r a s e l e v e l s among f i e l d a p p l i c a t o r s of c h o l i n e s t e r a s e - i n h i b i t i n g p e s t i c i d e s examples t h i s type of monitoring s i t u a t i o n . The outcome of medical monitoring i s the determination of the presence or absence of a medical marker of a t o x i c o l o g i c response to a s p e c i f i c workplace contaminant. The presence of a medical e f f e c t of overexposure leads to medical a c t i o n s aimed to i n t e r r u p t the t o x i c a n t ' s impact upon the worker's h e a l t h . Such medical a c t i o n s i n c l u d e appropriate medical therapy, medical removal p r o t e c t i o n , and medical advisements on the appropriateness of exposure l i m i t s . A p r o p e r l y designed b i o l o g i c a l monitoring program should be developed c o n j o i n t l y by the environmental engineer and medical s t a f f u t i l i z i n g environmental data about the nature of the workplace exposure and medical knowledge about the prevalence of medical c o n d i t i o n s that might a l t e r the s u s c e p t i b i l i t y of i n d i v i d u a l s to the environmental contaminant. The e v a l u a t i o n of the body's uptake of t o x i c a n t s which are done f o r environmental s u r v e i l l a n c e purposes can be used i n c o n j u n c t i o n w i t h medical f i n d i n g s to provide i n f o r m a t i o n on the v a l i d i t y of c u r r e n t assumptions about the human t o x i c i t y of the substance at exposure l e v e l s experienced i n the workplace. In the same manner, medical monitoring y i e l d s i n f o r m a t i o n which the environmental engineer can use along w i t h environmental measurements to judge the adequacy of i n d u s t r i a l hygiene p r a c t i c e s . I t i s e s s e n t i a l to formulate b i o l o g i c a l monitoring programs on the b a s i s of p r i o r environmental i n f o r m a t i o n about known or p o t e n t i a l workplace exposures to t o x i c a n t s s i n c e few m a t e r i a l s are s u f f i c i e n t l y unique to the workplace that b i o l o g i c a l monitoring can be undertaken without p r i o r documentation of the p o t e n t i a l f o r exposure. Assessments of o c c u p a t i o n a l exposure can be confounded by other environmental sources of t o x i c agents. For a metal such as a r s e n i c that can be absorbed from common seafood items i n the d i e t , p o t e n t i a l non-occupational sources should always be considered i n the development of b i o l o g i c a l monitoring programs ( 3 ) · The c o n s u l t a t i v e approach to the design of b i o l o g i c a l monitoring programs can a i d i n the determination of the type of s u r v e i l l a n c e that i s a p p r o p r i a t e . For i n s t a n c e , environmental data showing a c h r o n i c exposure t o Pb might lead to
In Chemical Hazards in the Workplace; Choudhary, G.; ACS Symposium Series; American Chemical Society: Washington, DC, 1981.
C H E M I C A L HAZARDS IN T H E W O R K P L A C E
228
e n v i r o n m e n t a l m o n i t o r i n g w i t h b l o o d Pb l e v e l s monitoring the l a t t e r Pb
( 4 ) , whereas e n v i r o n m e n t a l
intermittent surveillance
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acute
and m e d i c a l
for elevated blood zinc protoporphyrin l e v e l s since i s a s e n s i t i v e m a r k e r o f an e x c e s s i v e body b u r d e n o f findings consistent
w i t h low
exposures might r e s u l t i n e n v i r o n m e n t a l w i t h b l o o d Pb l e v e l s a l o n e t o m o n i t o r f o r
overexposures
(_5)·
As shown i n F i g u r e 1, t h e u s e o f b i o l o g i c a l m o n i t o r i n g i n e n v i r o n m e n t a l o r m e d i c a l s u r v e i l l a n c e programs s h o u l d b e g i n w i t h t h e s e l e c t i o n o f a t e s t w i t h an outcome t h a t i s a p p r o p r i a t e to the type of s u r v e i l l a n c e b e i n g conducted. For a d e s i g n a t e d workplace c o n t a m i n a n t , the v a l i d i t y of a b i o l o g i c a l m o n i t o r i n g p r o c e d u r e i s d e p e n d e n t upon (1) t h e s e n s i t i v i t y o f t h e t e s t , the p r o b a b i l i t y t h a t t h e t e s t r e s u l t w i l l be p o s i t i v e when t h e f a c t o r t o be m e a s u r e d i s p r e s e n t ; a n d , (2) t h e s p e c i f i c i t y o f t h e t e s t , t h e p r o b a b i l i t y t h a t t h e t e s t r e s u l t w i l l be n e g a t i v e when t h e f a c t o r t o be m e a s u r e d i s a b s e n t ; a n d , ( 3 ) t h e p r e s e n c e o f t h e p o t e n t i a l t o x i c a n t i n t h e w o r k p l a c e where m o n i t o r i n g i s c o n d u c t e d ; a n d , (4) i n the i n s t a n c e of m e d i c a l m o n i t o r i n g , the absence of o t h e r m a t e r i a l s i n the workplace t h a t might cause the same m e d i c a l e f f e c t t h a t t h e t o x i c a n t i s known t o c a u s e . The u s u a l b i o l o g i c a l m o n i t o r i n g t e s t i s an a s s a y of b i o l o g i c a l s p e c i m e n s (semen ( 6 ) , u r i n e (_3), b l o o d (]_)> and e x p i r e d a i r (8)). In e n v i r o n m e n t a l s u r v e i l l a n c e , a b i o a s s a y d i r e c t e d to the d e t e c t i o n of a s u b s t a n c e or i t s b i o t r a n s f o r m a t i o n product i s the u s u a l t e s t m e t h o d . S k i n s e n s i t i z a t i o n t e s t s (_9), p h y s i o l o g i c a l c h a n g e s i n p u l m o n a r y f u n c t i o n ( 1 0 ) , and c h a r a c t e r i s t i c e f f e c t s o f d u s t s on c h e s t x - r a y s (11) s u p p l e m e n t t h e u s e o f t h e b i o a s s a y i n m o n i t o r i n g f o r e a r l y m e d i c a l m a n i f e s t a t i o n s of exposure to hazardous substances. The j u d i c i o u s u s e o f b i o l o g i c a l m o n i t o r i n g e n t a i l s s c h e d u l e d a d m i n i s t r a t i o n of the t e s t w i t h i n the c o n t e x t
the of the
exposure h i s t o r y . The u s e f u l n e s s o f u r i n a r y c o n c e n t r a t i o n s of h e a v y m e t a l s , s u c h as u r a n i u m , c a n be h i g h l y d e p e n d e n t upon t h e t i m e between t h e c o l l e c t i o n o f t h e s p e c i m e n and t h e l a s t e x p o s u r e ( 1 2 ) . The a s s e s s m e n t o f b l o o d c h o l i n e s t e r a s e levels i s s i m i l a r l y d e p e n d e n t upon t h e t e m p o r a l r e l a t i o n s h i p between t h e a d m i n i s t r a t i o n o f t h e t e s t a n d t h e e x p o s u r e ( 1 3 ) . The d e s i g n a t i o n o f an e x p o s u r e o r m e d i c a l p a r a m e t e r as n o r m a l o r a b n o r m a l c a n be made i n r e l a t i o n s h i p t o t h e i n d i v i d u a l ' s b a s e l i n e s t a t u s 0,JL3) o r i n r e f e r e n c e t o r e s u l t s f r o m a s t a t i s t i c a l l y g e n e r a t e d r e f e r e n c e g r o u p (14,15). T e s t r e s u l t s t h a t show b i o a b s o r p t i o n o f t o x i c a n t s ( e . g . , b l o o d Pb l e v e l s ) o r r e v e a l e a r l y m e d i c a l e f f e c t s o f o v e r e x p o s u r e t h a t do n o t c o n s t i t u t e a d i s e a s e e n t i t y ( e . g . , b l o o d z i n c p r o t o p o r p h y r i n l e v e l s ) c a n be g i v e n t o t h e environmental engineer i n personally i d e n t i f i a b l e form. B i o l o g i c a l monitoring test r e s u l t s that i d e n t i f y a disease state (e.g. , oligospermia) constitute confidential information about the h e a l t h s t a t u s of the i n d i v i d u a l which i s not to be
In Chemical Hazards in the Workplace; Choudhary, G.; ACS Symposium Series; American Chemical Society: Washington, DC, 1981.
15.
MONROE
Biological
transmitted
outside the
Monitoring
the
test
for
Surveillance
m e d i c a l department
permission
of
subject.
personally
i d e n t i f i a b l e c o m p i l a t i o n s of
conclusionary
statements
environmental
engineer
so
about that
between w o r k p l a c e e x p o s u r e s
229
without
the
The p h y s i c i a n s h o u l d the
test
proper
such data results
as
with
correlations
and any m e d i c a l e f f e c t s
share well
nonas
the
c a n be made that
are
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discerned. Relationship
of
Surveillance
Activities
Biological
B i o l o g i c a l Monitoring
monitoring tests
are
to
Other
Medical
among t h e most
valuable
medical surveillance tools. A l t h o u g h g e n e r a l t e s t s o f body system f u n c t i o n , such as r e n a l f u n c t i o n t e s t s ( e . g . , b l o o d u r e a n i t r o g e n ) , a r e done on b i o l o g i c a l s p e c i m e n s and h a v e a r o l e i n m e d i c a l s u r v e i l l a n c e programs f o r o c c u p a t i o n a l exposure to s y s t e m i c t o x i n s (Jj5), t h e s e p r o c e d u r e s d i f f e r q u a l i t a t i v e l y f r o m b i o l o g i c a l m o n i t o r i n g t e s t s which s a t i s f y the f o u r c r i t e r i a described e a r l i e r for v a l i d b i o l o g i c a l monitoring procedures. A b i o l o g i c a l m o n i t o r i n g t e s t s h o u l d be a r e l i a b l e and v a l i d m e a s u r e o f a p a t h o p h y s i o l o g i c change i n c u r r e d by t h e a c t i o n o f a t o x i c s u b s t a n c e upon a s p e c i f i c m e t a b o l i c o r p h y s i o l o g i c pathway. The b i o l o g i c a l r e s p o n s e s h o u l d a p p e a r i n most a l l i n d i v i d u a l s exposed to u n s a f e l e v e l s of the h a r m f u l m a t e r i a l . F o r e x a m p l e , when cadmium i s t h e o n l y h e a v y m e t a l t o w h i c h workers are exposed, the e l e v a t e d u r i n a r y e x c r e t i o n of b e t a - 2 m i c r o g l o b u l i n i n cadmium i n t o x i c a t i o n r e f l e c t s a s e l e c t i v e a c t i o n o f cadmium upon r e n a l h a n d l i n g o f t h i s l o w m o l e c u l a r weight p r o t e i n (17). In t h e a b s e n c e o f e x p o s u r e t o o t h e r h e a v y m e t a l s w h i c h m i g h t c o n f o u n d t h e r e l a t i o n s h i p b e t w e e n cadmium and t h i s b i o l o g i c a l e f f e c t , the use of b e t a - 2 - m i c r o g l o b u l i n d e t e r m i n a t i o n s f o r b i o l o g i c a l m o n i t o r i n g p u r p o s e s i s b a s e d on the r e l a t i v e s p e c i f i c i t y of e l e v a t e d u r i n a r y e x c r e t i o n of t h i s p r o t e i n t o cadmium n e p h r o t o x i c i t y as w e l l as a n e x t r e m e l y h i g h p r e v a l e n c e o f t h i s a b n o r m a l i t y among p e r s o n s o v e r e x p o s e d t o t h i s metal. L i n c h i n c l u d e d p u l m o n a r y f u n c t i o n t e s t s and o t h e r n o n b i o a s s a y p r o c e d u r e s i n h i s compendium o f b i o l o g i c a l m o n i t o r i n g t e s t s (J_8). When a s t r o n g i d e n t i t y e x i s t s b e t w e e n a t o x i c a n t and a m e d i c a l e f f e c t , l a b o r a t o r y p r o c e d u r e s o t h e r t h a n a b i o a s s a y (pulmonary f u n c t i o n t e s t s , chest r a d i o g r a p h s , etc.) c a n be u s e d t o m o n i t o r t h e i n t e r a c t i o n between t h e t o x i c a g e n t and a p a r t i c u l a r p h y s i o l o g i c or m e t a b o l i c system. The d e m o n s t r a t i o n of an a c u t e f a l l i n v e n t i l a t o r y c a p a c i t y a f t e r TDI e x p o s u r e (10) and c a l c i f i e d p l e u r a l p l a q u e s a f t e r a s b e s t o s e x p o s u r e ( 1 1 ) example t h e u s e o f v a l i d n o n - b i o a s s a y p r o c e d u r e s t o monitor b i o l o g i c a l responses to workplace e x p o s u r e s . S i n c e c e r t a i n r e s p i r a t o r y a b n o r m a l i t i e s that are a s s o c i a t e d w i t h e x p o s u r e s t o d u s t s o r o t h e r r e s p i r a t o r y t o x i n s may be e a s i l y c o n f o u n d e d by o t h e r f a c t o r s , s u c h as c i g a r e t t e s m o k i n g ( 1 9 , 20,
In Chemical Hazards in the Workplace; Choudhary, G.; ACS Symposium Series; American Chemical Society: Washington, DC, 1981.
C H E M I C A L HAZARDS IN T H E W O R K P L A C E
230 21 ) ,
the
chest
x-ray
and p u l m o n a r y f u n c t i o n t e s t s
s h o u l d be
u s e d as a b i o l o g i c a l m o n i t o r i n g t e c h n i q u e when an e x p o s u r e t o a r e s p i r a t o r y t o x i n r e s u l t s i n a p a t h o p h y s i o l o g i c response that c a n be r e a d i l y a s c r i b e d t o t h a t m a t e r i a l . The f u l f i l l m e n t o f s i m i l a r c r i t e r i a s h o u l d be met b e f o r e t e c h n i q u e s o t h e r t h a n chest for
radiography
use
or
pulmonary p h y s i o l o g i c t e s t i n g
i n b i o l o g i c a l monitoring
are
adopted
programs.
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E c k h a r d t (22) h a s r e m a r k e d t h a t t h e e v o l u t i o n o f b i o l o g i c a l t e s t s to s c r e e n f o r the h y p e r s u s c e p t i b l e worker r e p r e s e n t s one o f t h e i m p o r t a n t p r e v e n t i v e h e a l t h v i s t a s i n occupational health. The d e v e l o p m e n t o f s e n s i t i v e and s p e c i f i c b i o l o g i c a l markers of e a r l y m e d i c a l sequelae of h a r m f u l exposures h o l d s promise to a l l o w the i d e n t i f i c a t i o n of i n a d e q u a t e e x p o s u r e c o n t a i n m e n t and u n s a f e e x p o s u r e l i m i t s b e f o r e i r r e v e r s i b l e impairment of h e a l t h has o c c u r r e d . Medical-Legal
Aspects
of
B i o l o g i c a l Monitoring
i n Medical
Surveillance As w i t h o t h e r m e d i c a l s u r v e i l l a n c e p r o c e d u r e s , t h e r e i s a m e d i c a l - l e g a l r a m i f i c a t i o n to the use of b i o l o g i c a l m o n i t o r i n g in medical s u r v e i l l a n c e . Medical surveillance i s a preventive medical a c t i v i t y that screens for hypersusceptible i n d i v i d u a l s and m o n i t o r s t h e h e a l t h e x p e r i e n c e o f p e r s o n s p r e s u m a b l y e x p o s e d t o s a f e l e v e l s o f s u b s t a n c e s known t o have t h e p o t e n t i a l t o c a u s e d i s e a s e . When s u c h m e d i c a l s u r v e i l l a n c e i s u n d e r t a k e n , t h e r e i s a p r e s u m p t i o n o f a r e l a t i o n s h i p between exposure to the p o t e n t i a l t o x i c a n t f o r which m e d i c a l s u r v e i l l a n c e i s b e i n g done and m e d i c a l c o n d i t i o n s t h a t a r e found to f i t the t o x i c i t y p r o f i l e of the a g e n t . For i n s t a n c e , the d i s c o v e r y of o l i g o s p e r m i a d u r i n g m e d i c a l s u r v e i l l a n c e f o r o c c u p a t i o n a l e x p o s u r e t o d i b r o m o c h l o r o p r o p a n e (DBCP) c o n s t i t u t e s r e a s o n a b l e m e d i c a l e v i d e n c e t h a t e x p o s u r e t o DBCP i s t h e c a u s e o f t h i s m e d i c a l f i n d i n g (6)· Outside the c o n t e x t o f m e d i c a l s u r v e i l l a n c e f o r o c c u p a t i o n a l e x p o s u r e t o DBCP a n d i n t h e a b s e n c e o f an o c c u p a t i o n a l h i s t o r y o f e x p o s u r e t o t h i s a g e n t , the varicocele The
most common c a u s e o f o l i g o s p e r m i a m i g h t or e n d o c r i n e d y s f u n c t i o n .
Informed The
be
a
Worker
necessity
for
the
worker
to
cooperate
i n the
conduct
o f b i o l o g i c a l m o n i t o r i n g p r o c e d u r e s i s e v i d e n t need f o r c o m m u n i c a t i o n t o o c c u r b e t w e e n t h e w o r k e r and t h e o c c u p a t i o n a l h e a l t h p r o f e s s i o n a l c o n d u c t i n g the program. The e x t e n t o f p a r t i c i p a t i o n w i t h i n a w o r k e r p o p u l a t i o n and t h e q u a l i t y o f c o m p l i a n c e among i n d i v i d u a l w o r k e r s m i g h t be e n h a n c e d by i n f o r m i n g p a r t i c i p a n t s o f t h e p u r p o s e o f t h e p r o g r a m and t h e a n t i c i p a t e d u s e o f t h e t e s t r e s u l t s . M o n i t o r i n g t h a t i s done f o r e n v i r o n m e n t a l and m e d i c a l s u r v e i l l a n c e d i f f e r s c o n s i d e r a b l y
In Chemical Hazards in the Workplace; Choudhary, G.; ACS Symposium Series; American Chemical Society: Washington, DC, 1981.
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15.
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in the meaning of the test result (acceptable exposure vs. unacceptable exposure; normal medical finding vs. abnormal medical finding). Therefore, it is of utmost importance to provide the worker with sufficient information about the program so that the value of participation can be understood and reasonable expectations can be developed about the outcome to be achieved from the test results. In particular, the purpose of biological monitoring procedures that are done to detect potential medical effects of workplace exposures should be discussed with the worker by the physician within the context of the exposure and present medical knowledge about the individual's health. Information about the relationship of the possible outcomes of the test and the meaning for the health of the individual, i.e., reversible or irreversible pathophysiology, should also be disclosed in detail before the biological monitoring activity is begun. Summary Biological monitoring is useful in environmental and medical surveillance activities. Its use in environmental surveillance is to provide the environmental engineer with information about the control of potentially harmful exposures. The function of biological monitoring in medical surveillance is to identify medical effects consequent to such exposures. Biological monitoring entails the bioassay or other measurement of toxicants or biotransformation products and medical markers that are altered by the presence of the toxicant (or its biotransformation products). By virtue of a predictive effect of the toxicant upon the pathophysiologic response measured, biological monitoring tests are among the most desirable of medical surveillance techniques. Because environmental monitoring relates to the matter of exposure and medical monitoring to the occurrence of medical abnormalities consequent to exposure, it is advisable to inform the worker of the purpose of the test that is to be done as well as to indicate beforehand the meaning of potential test outcomes. Acknowledgement Mrs. Lorraine Meyers and Miss Patricia Abbe are thanked for their help in preparing the manuscript. Literature Cited 1. Linch, A. L . , "Biological Monitoring for Industrial Chemical Exposure Control", CRC Press, Inc.: West Palm Beach, FL, 1974.
In Chemical Hazards in the Workplace; Choudhary, G.; ACS Symposium Series; American Chemical Society: Washington, DC, 1981.
232
CHEMICAL HAZARDS IN THE WORKPLACE
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2.
Final Rule on Access to Employee Exposure and Medical Records, 29 CFR part 1910, Federal Register, 1980, 45, 35212-35303. 3. Schrenk, H. H.; Schreibes, L., Urinary Arsenic Levels as an Index of Industrial Exposure, Am. Ind. Hyg. Assoc. J., 1958, 19, 225-228. 4. Eisinger, J.; Fischbein, Α.; Blumberg, W. E.; Lilis, R.; Selikoff, I. J., Zinc Protoporphyrin in Blood as a Biological Indicator of Chronic Lead Toxication, J. Environ. Pathol. Toxicol., 1978, 1, 897-910. 5. Cavalleri, Α.; Minoia C.; Pozzoli, L.; Baruffini, Α., Determination of Plasma Lead Levels in Normal Subjects and in Lead-Exposed Workers, Br. J. Ind. Med., 1978, 35, 21-26. 6. Whorton, D.; Krauss, R. M.; Marshall, S.; Milby, Τ. Η., Infertility in Male Pesticide Workers, Lancet, 1977, 2, 1259-1261. 7. Wills, J. Η., The Measurement and Significance of Changes in the Cholinesterase Activities of Erythrocytes and Plasma in Man and Animals, CRC Crit. Rev. Toxicol., 1972, 1, 153-202. 8. Breysse, P. Α.; Bovee Η. Η., Use of Expired Air-Carbon Monoxide forCarboxyhemoglobinDetermination in Evaluating Carbon Monoxide Exposures Resulting from the Operation of Gasoline Fork Lift Trucks in Holds of Ships, Am. Ind. Hyg. Assoc. J., 1979, 30, 477-483. 9. Rostenberg, Α.; Bairstow B.; Luther T. W., A Study of Eczematous Sensitivity toFormaldehyde,J. Invest. Dermatol., 1952, 19, 459-462. 10. Wegman, D. H.; Pagnotto, L. D.; Fine, L. J.; Peters J. Μ., A Dose-Response Relationship inTDIWorkers, J. Occup. Med., 1978, 16, 258-260. 11. Edge, J. R., Asbestos Related Disease in Barrow-inFurness, Environ. Res., 1976, 11, 244-247. 12. Lippmann, M.; Ong, L. D. Y.; Harris, D. Β., The Significance of Urine Uranium Excretion Data, Am. Ind. Hyg. Assoc. J., 1964, 25, 43-54. 13. NIOSH Criteria Document for Occupational Exposure to Carbaryl, U.S. Department of Health, Education, and Welfare, September 1976; p.85. 14. Kowal, Ν. E.; Johnson D. E.; Kraemer,, D. F.; Pahren, H. R., Normal Levels of Cadmium in Diet, Urine, Blood, and Tissues of Inhabitants of the United States, J. Toxicol. Environ. Health, 1979, 5, 995-1014. 15. Rider, J. Α.; Hodges, J. L.; Swader J.; Wiggins, A. D., Plasma and Red Cell Cholinesterase in 800 "Healthy" Blood Donors, J. Lab. Clin. Med., 1957, 50, 376-383. 16. NIOSH Criteria Document for Occupational Exposure to Inorganic Mercury, U. S. Department of Health, Education, and Welfare, 1973; p. 2.
In Chemical Hazards in the Workplace; Choudhary, G.; ACS Symposium Series; American Chemical Society: Washington, DC, 1981.
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17. Piscator, Μ., Proteinuria in chronic cadmium poisoning 2. The applicability of quantitative and qualitative methods of protein determination for the demonstration of cadmium proteinuria, Arch. Environ. Health, 1962,5, 325-332. 18. Linch, A. L . , "Biological Monitoring for Industrial Chemical Exposure Control", CRC Press, Inc.: West Palm Beach, FL, 1974; p. 4. 19. Krumholz, R. Α.; Chevalier R. B.; Ross, J. C., Changes in Cardiopulmonary Functions Related to Abstinence from Smoking - Studies in Young Cigarette Smokers at Rest and Exercise at 3 and 6 Weeks of Abstinence, Ann. Intern. Med., 1965, 62, 197-207. 20. Weiss, W., Cigarette Smoking and Diffuse Pulmonary Fibrosis, Arch. Environ. Health, 1967, 14, 564-568. 21. Theriault, G. P.; Peters, J. M.; Johnson, W. Μ., Pulmonary Function and Roentgenographic Changes in Granite Dust Exposure, Arch. Environ. Health, 1974, 28, 23-27. 22. Eckardt, R. E., Evaluation of the Worker - Tools and Techniques for the Future, Am. Ind. Hyg. Assoc. J., 1964, 25, 126-132. RECEIVED September
19, 1980.
In Chemical Hazards in the Workplace; Choudhary, G.; ACS Symposium Series; American Chemical Society: Washington, DC, 1981.