Document 8Vkxa0w425Ra86ZyaM2egEbLo
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THE NEW ENGLAND JOURNAL O F MEDICINE
March 1. 19%
MEDICAL PROGRESS
OCCUPATIONAL MEDICINE (First of Two Parts)
MARK R. CULLENM, .D., MARTIN G . CHERNIACKM,.D.. AND LINDA ROSENSTOCLKM, .D., M.P.H.
THE clinical discipline of occupational medicine, largely unstudied, untaught, and unpracticed in major medical centers as recently as a decade ago, underwent unprecedented rejuvenation in the 1980s. Spurred by national regulatory programs and requirements, widespread litigation concerning toxic injury, and an altered public perception of environmental risks, the demand for the services of occupational medicine has risen sharply, especially outside the workplace.' An outgrowth of this increase in demand has been an explosion of new investigations and new information as the field rejoins the mainstream of medicine, as well as new academic faculties, journals,
and $rainingprograms.
The goal of this article is to describe and review some of the new knowledge about clinical occupational medicine. Given the breadth of the subject, we cannot discuss every important topic in occupational medicine; instead, we shall attempt to cover the areas most relevant to clinical practice, emphasizing those that tend to be ignored in the nonspecialized medical literature. In a few instances, we discuss major advances involving less common disorders, because of their conceptual importance to developments in the field as a w i d e .
SPECTRUM OF OCCUPATIONAL DISEASEIN THE UNITED STATES
Ideally, this review would begin with a summary of the latest data on the prevalence of each occupational disease, highlighting temporal and geographic trends. Such data would be invaluable to clinicians in recognizing and treating common problems, just as similar data have been useful in the management of communicable diseases. Unfortunately, despite the upsurge in practice and research, reliable surveillance for occupational diseases began only in the late 1980s. Case definitions have not yet been agreed on for most common conditions, and strategies and resources to develop reporting schemes remain severely limited.* Precise data are unavailable, and estimates of prevalence and incidence (for example, that 125,000ifatalities occur annually due to occupational disease as a result of 500,000incident cases) are neither based on verifiable quantitative data nor specific enough to facilitate their use by practitioner^.'.^
From the Yale-New Haven Occupational Medicine Rograrn. Yale University School of Medicine, New Haven, Conn. (M.R.C.. M.G.C.). and the Occupational Medicine &gram. Universityof WashingtonSchool of Medicine. Seaale (L.R.). Address reprint requests to Dr. Cullen at the Occupational Medicine
Program. 333 Cedar St.. New Haven. CT 06510.
Some fragmentary data have been developed in recent years that may offer general guidance. A crude ranking of the relative prevalence of occupational diseases in regions dominated by manufacturing, shipbuilding, and general construction may be inferred from a recent report from Connecticut (Fig. I).' Viewed another way, the same data offer insight into the most common causes of occupational disease in this region dominated by manufacturing and construction: asbestos, organic solvents and oils, plastics, and repetitive trauma.
The types of hazardous exposures evaluated and the occupational diseases diagnosed at the Universiv of Washington Occupational Medicine Clinic in Seattle were similar to those in Connecticut. Among the 1424 patients evaluated in the Seattle diagnostic clinic during a five-year period (1982 to 1987), 881 (62 percent) were found to have one or more workrelated conditions. The most prevalent conditions were asbestosis (n = 312), asbestos-induced pleural disease without asbestosis (n = 127), noise-induced loss of hearing (n = 132),upper respiratory irritation, including bronchitis (n = 114), acute and chronic intoxication with solvents (n = 70), occupational asth-
ma (n = 67), other respiratory conditions (n = G),
and carpal tunnel syndrome (n = 33). Using all avail-
able information, including an interviewer-administered occupational history, an industrial hygienist assigned up to four hazardous-work exposures to each patient; the most prevalent exposures were to asbestos (53 percent), noise (49 percent), solvents (42 percent), welding fumes (35 percent), fibrous glass ( 11 percent), vibration (9 percent), and lead (4 percent).
Dermatoses and injuries due to repetitive trauma are probably severely underrepresented in these case series because of limited referrals from specialists with long experience of these occupational disorders. The role of occupation in the genesis of multifactorial chronic diseases (such as heart disease and cancer) is also likely to be underestimated in such series. These limitations and the lack of rigorous diagnostic criteria notwithstanding, the most common occupational diseases almost certainly include the asbestos-related disorders, industrial bronchitis and asthma, intoxication with organic solvents, upper respiratory and ocular irritation, noise-induced loss of hearing, and musculoskeletal dysfunction due to repetitive trauma. Important but less frequent disorders are heavy-metal
poisoning (especially lead poisoning), silicosis, toxic
hepatitis, and dysfunctional psychological reactions to
exposures and accidents in the workplace. No comparable clinical series have been reported
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-OCCUPATIONAL MEDICINE CULLEN ET AL.
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DiaanOSlS
Figure 1. The 20 Most Common Occupational Diseases Diagnosed at the Yale Referral Clinics in New Haven and New Lon-
don, Connecticut, between 1979 and 1987. The calculations are based on the average number of new cases annually. Cases of contact dermatitis, low-back strain, and carpal tunnel syndrome are underrepresentedbecause of referral bias. Cases of industrial bronchitis and bronchogenic carcinoma are underrepresentedbecause of the counting methods. See text for
a description of multiple chemical sensitivities. Calculated on the basis of data from Cullen and Chernia~k.~
from regions of the country dominated by mining activities. There is clear documentation, however, that despite the regulations imposed by the Mine Safety and Health Act of 1969, which limit dust levels in underground and surface mines, both pneumoconiosis of coal workers5 and silicosis6 remain endemic in the United States, and new cases still occur, although less frequently than in the past. The reasons include noncompliance with standards, long latency from first exposure to the onset of disease, and presumably, enhanced detection because of mandated examinations and an increased awareness of occupational diseases. What remains to be proved is whether mining standards, based largely on the experience of the United Kingdom and Europe, will be effective in preventing new cases among younger workers who are exposed only to the lower levels of coal and quartz dusts mandated by regulations enacted nearly 20 years ago. Early U.S. data'.' suggest that the coal standard may protect those who work with bituminous coal. but concern about those who work with the more pathogenic anthracite coal. mostly in the eastern United States, remains high.8
Data on the occurrence of occupational diseases in agricultural regions are scarcest of all. although the available data on work-related mortality rates in this
sector show that agriculture and mining compete as the two most dangerous occupation^.^ Pesticides and herbicides can produce both acute and chronic disorders," but how often these come to medical attention is unknown. Although rates of traumatic injury are known to be very high in this s e ~ t o rt,h~e medical consequences of repetitive trauma among agricultural and wood-products workers have been delineated only in lumbering, in which vibration-related disorders are ubiquitous." The unique, diverse, and potentially serious effects of exposure to animal and vegetable products in the food-processing industry, especially on the respiratory tract, have recently been reviewed," but quantitative data and regional variation remain unreported.
Although the influence of occupational diseases on overaII regional morbidity and mortality cannot be readily inferred from case series and data on specific exposures, population studies of respiratory disease suggest that workplace factors may be important. For
example, the results of the Harvard Six Cities Study
demonstrate significant increases in both chronic respiratory symptoms and functional abnormalities related to occupational exposure to dust, fumes, and gases, after adjustment for smoking habits and the level of ambient air p ~ l l u t i o n .S' ~uch exposures were reported by half or more of the adults in every region of the United States studied. If occupational factors contribute even a small fraction of the rates of nonrespiratory illnesses, as our case series suggest, then occupational disorders are very prevalent.
OSPECIFIC CCUPATIONAL DISORDERS
Lung Diseases
The most frequently diagnosed work-related conditions in industrial regions and the best-established medical consequences of mining and farming involve the lower respiratory tract, because it is the most important portal of entry for toxic agents from the work environment. The health consequences of exposure to asbestos, the recognition of which paved the way for much of the resurgence of interest in occupational medicine, have been widely reported and reviewed l4 and will not be discussed further.
New data and insight have emerged in recent years regarding silicosis, the most prevalent chronic OCcupational disease in the world and stubbornly resistant to eradication in the United States. The disorder has been specifically targeted in the Centers for Disease Control's prevention objectives for 1990.15 Although silicosis is classically associated with the mining of hard rock, anthracite coal, and metals, high rates of the disease have been reported in foundries, brickvards, glassmaking, ceramic manufacture, and industrial sandblasting.6 Particularly aggressive outbreaks have been seen in the silica-flour and stone-processing industries; cases occur within a few years of the first exposure, and many advance rapidly to progressive massive fibrosis.I5,l6
Beyond the public health efforts mentioned, some
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THE NEW ENGLAND JOURNAL OF MEDICINE
March I . 1390
progress has been made in the past decade that can benefit physicians evaluating new cases and following up patients with established disease. Diagnostically, it appears that no strategy will soon replace the triad of careful assessment of past exposure, exclusion of masqueraders (for example, sarcoidosis
and eosinophilic granuloma), and -more often as the
disease becomes less common - pathological eval-
uation of tissue. Noninvasive procedures, including bronchoalveolar lavage, l 7 computerized tomography of the chest,'* and determinations of serum angiotensin-converting-enzyme activity, have not demonstrated any strongly positive or negative predictive value. Long-term management has not become easier. Newer evidence supports the conclusion that silicosis can progress, even to massive fibrosis, despite the elimination or reduction of exposure.20Tuberculosis continues to complicate both simple silicosis (without massive fibrosis) and advanced disease*'; short courses of antitubercular therapy have been
proposed,'2 but their efficacy is not established. An elegant study has implicated anaerobic bacteria in
the superinfection affecting patients with advanced silicosis23;these patients may present with the sudden cavitation of coalescent masses historically ascribed to either mycobacteria or ischemia. The proper management of patients with silicosis will also involve consideration of the excessive occurrence of lung
carcinoma^.^'^^^^^^ Although the epidemiologic relation
between silica and cancer is still being explored (since other toxins in mines and foundries may be responsible),26*27 the possibility that it may be a tumor must now be considered when a new lung nodule develops
in an affected patient - not a trivial task in patients
who already have underlying extensive and coalescing pulmonary nodules.
The future control and treatment of silicosis may be aided by cellular and molecular research. The central role of pulmonary macrophages, both in clearing silica and in elaborating chemoattractants for polymorphonuclear leukocytes and fibroblasts, seems establ i ~ h e d ' ~ , 't~he; precise sequence of events, probably involving interleukin- 1,29 is now being unraveled. Already, experiments with cell-specific and mediator-
specific inhibitors are under way in animal model^,^^.^'
offering some hope that the prevention of secondary disease may become part of the ongoing effort to eradicate this preventable disease.
Beyond the pneumoconioses and their sequelae, the most important progress against occupational lung disease in recent years has been in the area of immunologically mediated disorders of the airways and parenchyma. Our knowledge of occupational asthma, probably the most prevalent of these disorders in developed co~ntries,~ha' s expanded con-
siderably because patients and physicians are increasingly aware of environmental factors and because new forms of technology exist for studying its mechanisms. Although debate continues on a uniform definition of the disease, and although its incidence in most
industries remains unknown." consensus has bee., reached on several issues.
A broad array of natural and synthesized chemicals are potential asthmogens; these include many small molecules. such as toluene diisocyanate and plicatlc acid, and larger protein antigens. such as baccefiai enzymes, animal proteins, and grains. The list of documented causal agents has expanded rapidly in thr past five years (Table 1).33-51Many of the established causal agents appear in an extraordinarily diversr range of materials and processes, often as unlabeled minor constituents or contaminants. Finding specific culprits or excluding them from a patient's environment may therefore be very challenging. In many cases, this is less important than documenting temporal changes by examination, spirometry, or peak flowmetry that implicate some causal factor from which the patient can be removed.
Multiple mechanisms appear to be involved in inducing and sustaining occupationally induced asthma. In general, the larger molecules seem to act most frequently through classic IgE-mediated mechanisms, affecting atopic workers (especially smokers) more commonly.32Radioallergosorbent testing has been of
some use in identifying those sensitized in this way.+2-j2 The action of the smaller molecules typically does not involve the same host predisp~sition,j'.a~n~d studies have not reproducibly demonstrated antibodies to these agents or agent-protein complexes in affected patients, despite considerable ~earching.'~.'' Mechanisms involving the local release of bronchoactive mediators seem p l a ~ s i b l e , j ' *al~th~o~ug~h~the characteristic differences between hosts in susceptibility and
usual onset after repeated exposure remain unexplained by nonimmunologic mechanisms.
Although demonstrating a pattern of symptoms and signs consistent with occupational factors is usually possible, confirmatory tests for occupational asthma are not generally available. Work by Pepys and Hutchcroft" and Hendrickjg suggested that an inhalation challenge with the suspected agent would be a sensitive and specific diagnostic tool, but subsequent experience has uncovered drawbacks for both the patient and the diagnostician; reactions in the IaboratoV sometimes dangerously exceed those in the worlcplace,60.6'and for some agents, the test is very insemitive.62
Most important, several longitudinal clinical studies have refuted the long-held dogma that OccupatioJla1 asthma typically reverses after a patient is removed from exposure. Experience with western red cedZir (plicatic acid), toluene diisocyanate, and other smd1molecule agents plainly demonstrates that at least half of all patients will surer persistent, even progressive
asthma despite recognition and removal from exPo-
SUre.ti1.ti3-lMEvidence suggests that the duration or symptoms before removal is a strong prognostic i d ' -
cator; a period longer than six months is genenllv predictive of the persistence of disease. Although the mechanism is highly speculative, the clinical imPerA-
Vol. 322 NO. 9
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VEGETABLE
OCCUPATIONAL MEDICINE -CULLEN E T AL.
Table 1. Materials Causally Linked to Asthma in the Workplace.
ANIMAL
Danders Insects Silkwom larva Shellfish Pig or chicken excreta Fish feed Animal enzymes
PLASTIC OR CHEMICAL
Acid anhydrides Epoxy resins Diisocyanates Persulfates Para-phenylemdiamine Phthalic anhydride Dimethyl ethanolamim Azobisformamidc Azodicahnamidc Formaldehyde Ethylenediamine Acrylates Henna
METAL
Stainless sreel Galvanized srcel Aluminum fluoride Vanadium Cobalt Tungsten carbide (cobalt) Platinum salts Nickel Chromium
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PHAWACEUTICAL
Penicillins Ceph.losp0rins Piperazine Psyllium Mehyldopr Spiramycin Teuacyclinc Amprolium Cimctidine Isoniazid Phenylglycine
tive to remove patients from exposure if suspicion exists now seems unequivocally justified.
Perhaps even more surprising - and of great concern given the ubiquity of these agents - is recent
evidence that persistent asthma may also result from exposure to workplace animal-protein asthmogens. Despite the conventional wisdom that bronchial hyperreactivity will disappear within months after the end of exposure to agents eliciting classic IgE-mediated bronchoconstriction, our own clinical experience
and a long-term follow-up of patients with crab-in-
duced asthma& suggest disease patterns similar to
those observed with the smaller chemical agents. Extrinsic allergic alveolitis, or "farmer's lung,"
which is characterized by recurring episodes of fever, chills, and pulmonary infiltrates, has also been the focus of renewed interest. Bronchoalveolar lavage, together with new techniques for identifying lymphocyte subpopulations, has helped elucidate the fundamental role of T lymphocytes in the di~order.~A'lthough diagnostic efforts focused historically on finding IgG antibodies against offending agents, the standard approach is now the demonstration of intense alveolar
lymphocytosis in lavage fluid. The cells, which are almost entirely of the T-cell class, are mostly suppressor cells, as shown by monoclonal-antibody labeling.67968In the appropriate clinical context, this combination is almost pathognomonic for the disorder, readily distinguishing it from sarcoidosis (in which helper cells predominate) and idiopathic pulmonary fibrosis (in which polymorphonuclear cells are most frequent). Humoral immunity probably contributes
to the pathogenesis as well, since IgM and IgG anti-
uks against the offending agents are frequently
round in lavage fl~id.~"'" These diagnostic advances have allowed the recog-
nition of new classes of agents in the workplace that Qn induce allergic alveolitis. To the broad range of molds and spores have now been added synthetic chemicals, most notoriously the diisocvanates in most J'"urethane paints. foams. and coatings.".'' Components of other plastics. especially epoxies. have also
been i n ~ r i m i n a t e dm, ~a~king it likely that many reactive synthetic chemicals cause the disorder. Curiously, the now well-characterized disease associated with plastics appears to have a more insidious natural history than the traditional farmer's lung or "humidifier fever." Some patients have presented without the typical acute syndrome (fever or leukocytosis, for example) and have responded more slowly to removal from exposure alone. Weeks or months of treatment with systemic steroids may be required as the inflammatory '
response and restrictive lung dysfunction ~lear.~'.~'
Information on the respiratory effects of cotton dust
has also grown. The historical description of byssinosis emphasized the peculiar temporal pattern of chest tightness, cough, and wheeze, which occurred dramatically on Mondays, after a weekend of no exposure, and diminished during the succeeding days. Recently, syndromes other than classic byssinosis have been recognized and classified. These include "mill
fever" - a self-limited, influenza-like reaction to initial exposure to dust - and a rarer pattern involving
the progressive bronchoconstriction typical of occupational asthma.74Although the relation between expo-
sure and acute effects has been widely accepted, conflicting data have unfortunately been published about
late risks, including chronic bronchitis and obstructive impairment. Updated longitudinal studies of cotton workers have shown dust-related excesses of severe o b s t r ~ c t i o n ,th~u~s,c~on~firming earlier work,77whereas autopsies have failed to show pathologic effects beyond those attributable to smoking." The recent demonstration of proteolytic enzymes in cotton7' provides a plausible mechanism for long-term effects, but the debate continues. Vigorous debate also surrounds the search for the causal agent or agents in the cotton bract that are responsible for the acute byssi-
notic effects. Considerable evidence. both experimental and epidemiologic, has incriminated endotoxin from contaminating bacteria as the agent of disease.Ho-8O:1n the other hand, Douglas and colleagues have demonstrated clear-cut bronchoconstrictor responses on inhalation challenge with dust rendered
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THE NEW ENGLAND JOURNAL OF .MEDICINE
March I , i g ~ ,
free of endotoxin; they continue to propose a heatstable, water-soluble component of the bract as the
Finally, remarkable insight into environmental dis-
ease has emerged from the study of chronic beryllium
disease, a serious, if uncommon, occupational lung
disorder that has puzzled clinicians and scientists for
decades. The disorder was first recognized in the
1940s in the metal-processing, nuclear, and fluores-
cent-light industries, and by 1950 voluntary controls
were imposed in the United States with dramatic
effect.85The number of cases of this sarcoidosis-like
disease dropped precipitously - even as the use of beryllium in industry expanded widely -despite in-
adequate knowledge of its mechanism and contradic-
tory epidemiologic data showing that attack rates in
some industries with relatively low levels of beryllium
in the air were higher than in other industries with
higher levels.86This victory of industrial hygiene illus-
trates the value of control, even in the face of biologic
uncertainties.
Unfortunately, despite controls in industry, new
outbreaks of berylliosis have recently been reported
in aircraft, metal-smelting, and nuclear plant^.'^*^^
Bronchoalveolar-lavage studies in cases from these
clusters and in previously diagnosed cases have re-
vealed intense T helper-cell lymphocytosis, as in
sarcoidosis. The two diseases, however, can be differ-
entiated with lymphocyte cultures of the lavage ma-
terial and peripheral blood; recent studies have docu-
mented specific in vitro reactivity to beryllium salts
'in patients with chronic beryllium disease, but not
s a r c o i d o s i ~ . ~T~he* ~sensitivity of the proliferative
response of lung lymphocytes to beryllium appears
to be high (unlike earlier experience with periph-
eral lymphocytes), rendering the test highly useful
for diagnosis and clinical
The ability to
diagnose the disease specifically has in turn helped
to define a dose-response relation for beryllium in dif-
ferent settings.*' Ultimately, immunologic and per-
haps new molecular tools may allow the early recog-
nition of those at risk for this idiosyncratic disease.
In this way, appropriate controls to protect an esti-
mated 800,000 U.S. workers could include more pre-
cise limits on exposure and could be reinforced by a
medical strategy to prevent the full expression of the
disease should workers become sensitized or otherwise
susceptible.
Renal Disorders
Because of the considerable amount of intrinsic renal disease whose origin is unexplained and because of the role of the kidney in detoxification and filtration,
-new methods for evaluating industrial nephrotoxicity
continue to be e ~ p l o r e d . ~T'wo nephrotoxins lead
and organic solvents -have been the targets of exten-
sive investigation. Although lead poisoning sufficient to cause direct renal injury occurs only rarely in the United States,92moderate exposure remains comrnon-
place among foundry workers, battery makers, glass and ceramics workers. and those who weld, burn, or sand painted metal or wood. This fact, combined with the concern over past accumulations, has focused attention on the interaction of small accumulations of lead with hypertension and gout, two conditions frequently but not invariably associated with renal disease. Batuman and others have provided provocative data suggesting that among patients with hypertensiong3 or gout% much of the variability in glomerular function can be explained by body lead levels. estimated by measuring urinary lead excretion for 72
hours after a challenge injection of calcium EDTA.
Batuman et al. infer from their findings that lead indirectly causes serious renal injury at doses far below its recognized nephrotoxic level; this inference may be premature in the light of each study's cross-sectional design and the lack of animal models to explain the role of lead. Nonetheless, the prevalence of hypertension and gout in the population and the ubiquity of lead (although it is generally well controlled in the modem workplace) make the hypothesis extremely important.
Organic solvents, such as trichloroethylene, carbon tetrachloride, and toluene, have long been recognized as causes of renal tubular injury, but recent data and the reinterpretation of previous findings implicate this wide class of agents as potentially important causes of acute and chronic glomerular di~ease.'~-'N~umerous case reports have linked exposure to solvents and gasoline with anti-glomerular basement membrane antibody glomerulonephritis alone or in conjunction with pulmonary hemorrhage (Goodpasture's syndrome)
A review of nine case-control studies exploring the relation between exposure to solvents and various types of glomerulonephritis found that all but one supported the association; in the five positive studies in which risk could be systematically calculated, a 2.8- to 8.9-fold higher risk was found among persons exposed to s01vent.~' O n the other hand, the cross-sectional evaluation of various exposed groups has failed to demonstrate more than minor differences in function as compared with control groups, and observed abnormalities have not been consistently referable to glomerular functioning, as was h y p o t h e s i ~ e d . ' ~ ~ - ' ~ Although anti-glomerular basement membrane antibody glomerulonephritis has been experimentally induced by mercuric chloride,llo*lll no solvent-induced model has been demonstrated. Experimental exposures to solvent have, however, been reported to cause glomerular lesions, although usually with tubulointerstitial injury."z~''6
Hematologic Disorders
Although toxic levels of workplace chemicals have
long been known to affect circulating blood elements
-- producing, for example, hemolysis due to lead Or
arsine or methemoglobinemia due to nitrites'17 at-
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OCCUPATIONAL MEDICINE - CULLEN ET AL.
599
tention has turned in recent years to possible long-
term, irreversible changes in bone marrow, especially
rnveloproliferative disorders. Much attention remains
&used on benzene, because it is ubiquitous (gasoline
is up to 3 percent benzene) and because it serves as a
useful disease
For many years it has been
known that workers exposed to benzene - especially
[hose involved in the production of petrochemical and
rubber goods and other work using mixed organic sol-
vents - are at risk for bone marrow suppression,
acute leukemia, and chronic myelogenous leuke-
mia.119,'20 Although regulation has reduced exposure
considerably, concern remains about the effects of the
low-level contamination of other solvents, petroleum
products, and chemicals with benzene. Recent labora-
tory advances include the first reproducible animal
model of chronic myelogenous leukemia (but not yet
of acute leukemia).121,'2I2n addition, the effects of
benzene metabolites on target bone marrow cells at
the cellular and molecular levels have been partially
elucidated. They include covalent bonding to DNA,
forming DNA adducts with the inhibition of RNA
synthe~is,"~and a slowly reversible decline in the
number of stem cells, measured as colony-forming
units in the spleen or in c u 1 t ~ r e . lT~h~e relation be-
tween these demonstrated effects and the evolution of
irreversible alterations in the marrow remains unex-
plained, as does the apparent variability in host re-
sponses to benzene, long noted in humans'25 and re-
cently observed in a population of homogenic rats.122
More immediately relevant from the perspective of
public health are new data on quantitative risk. Al-
though controversy still exists, Rinsky and colleagues
recently demonstrated a strong linear dose-response
relation between benzene and leukemia, with a sub-
stantial excess leukemia risk among people exposed to
less than 10 ppm, the standard set by the Occupation-
al Safety and Health Administration until recently.IzG
In the light of the longstanding difficulty of producing
cancer in animals, even with very high doses of ben-
zene, these findings suggest that humans are consider-
ably more sensitive than laboratory animals and cur-
rent testing systems to the effects of benzene.
Mounting evidence that another group of wide-
ly used solvents, the ether derivatives of ethylene
glycol, may also be myelotoxic provides a disturbing
Parallel. Ironically, these derivatives are now used as
substitutes in many printing, painting, coating, and
cleaning operations that once depended on benzene.
In addition to the demonstration of depressed cell
Counts in toxicity studies in ani mal^,'^',"^ several
well-studied cases of aplastic anemia in human^'^^`^^^
and a cross-sectional survey of painters showing a
15 percent prevalence of hypoproliferative anemia
Or n e ~ t r o p e n i a 'l~en~d credence to this suspicion.
The long-term consequences of the use of ether de-
rivatives are unknown. as are strategies for medical
Intervention, other than reducing exposure wherever
effectsare observed.
REFERENCES
I . Cullen MR. Roxnstock L. The challenge of teaching occupational and environmental medicine in internal medicine residencies. Arch lntcrn Mcd 1988: 148:2401-4.
2. Pollack ES. Keimig DG. eds. Counting injunes and illnesws in the workplace: proposals for a better system. Washington. D.C.: National Academy Res,1987.
3. Division of Health Romotion and Diseasc Revention, Institute of Mcdicine. Role of the primary care physician in occupational and environmental medicine. Washington. D.C.: National Academy Res. 1988.
4. Cullen MR, Cherniack MG. Spectrum of occupaLional di- in an academic hospital-based rcferral center in Connecticut from 1979 to 1987.
Arch Intern Med 1989; 149:1621-6. 5 . Anfield M. Reger R, Glenn R. The incidence and progression of p n c u m
coniosis over nine years in U S .coal miners. 1. Principal findings. Am J Ind Med 1984; 6:407-15. 6. Landngan PJ. Silicosis. State Art Rev Occup M d 1987; 2319-26. 7. Athonx R, Attfield M, Kellie S. Use of data from the x-ray scrtcning program for coal workers to evaluate effectiveness of the 2mg/M' c o d dust standard. J Occup Med 1986; 28:741-5. 8. Amandus HE, Hanke W.Kullman G. Reger RB. A rc-evaluation of mdiological evidence from a study of U.S. strip cool mincrs. Arch Envim Health 1984. 39346-51. 9. National Safety Council. Accident facts. Chicago: National Safety Coun-
cil, 1981235-8.
IO. Brown SK,Ames RG. Mengle DC.Occupational illnesxs from cholines-
terase-inhibiting pesticides among agricultural applicators in California 1982-1985. Arch Environ Health 1989; 4 4 3 - 9 . 11. Farkkila M, Pyykko 1, Jantti V, Aatola S.Starck 1. Korhonen 0. Forrstry workers exposed to vibration: a neurological study. Br 1 Ind Mcd 1988; 45: 188-92.
-'12. Merchant JA. Agricultural exposures to organic dusts. State An Rev OcCUP Med 1987; 2409-25. 13. Kom RJ, Dockcry DW, Spcirer FE,Ware JH, Fems BG Jr. Occupntiod exposures and chronic respiratory symptoms: a population-brsed study. Am Rev Respir Dis 1987; 136:298-304. '14. Mossman BT. Gee JBL. Asbestos-nlated diseases. N Engl J Mcd 1989;
-320 1721-30.
15. Silicosis South Dakota. Wisconsin. MMWR 1983: 32318-9.
' 16. Silica flour: silicosis (crystalline silica). NIOSH cumnt intelligence bulletin. No. 36. Cincinnati: National Institute for Occupational Safety and
Health. 1981. (DHHS (NIOSH) publication no. 81-137.)
s 17. Rom WN. Bitterman PB, Rennard Si. Cantin A, Crystal RG.Characteriza-
tion of the lower respiratory tract intlammation of nonsmoking individuals with interstitiallung disease associated with chronic inhalationof inorganic
- dusts. Am Rev Respir Dis 1987; 136:1429-34. 18. Begin R. Bergeron D. Samson L. Boctor kl.Cantin A. CT assessment of
. silicosis in exposed workers. Am J Radio1 1987; 148509-14. 19. Bucca C, Veglio F. Rolla G . et al. Serum angiotensin converting enzyme (ACE) in silicosis. Eur J Respir Dis 1984, 65:477-80. 20. Ng TP, Chan SL, Lam KP. Radiologic progression and lung function in silicosis: a ten year follow-up study. Br Med J 1987; 295:1&8. -21. Wosterholm P. Ahlmark A, Maasing R, Segelberg 1. Silicosis and risk of
lung cancer or lung tuberculosis: a cohort study. Environ Res 1986;
4 1:339-50. ' 22. E s c m t BC. Langton ME. Cowie RL. Short-course chemotherapy for sili-
co-tuberculosis. S Afr Med J 1984: 66:327-30.
23. del Campo JM, Hitato J, Gea G, et al. Anaerobes: a new aetiology in cavitary pneumoconiosis. Br J lnd Med 1982; 39392-6.
1 24. Finkelstein M. Liss GM, Krammer F. Kusiak RA. Mortality among workers receiving compensation awards for silicosis in Ontano, 1940-85. Br J Ind Med 1987: 44:588-94.
* 25. Zambon P.Simonaro L. Mastrangelo G . Winkelmann R, Saia B, Crcpct M. Mortality of workers compensated for silicosis during the period 195963 in the Veneto region of Italy. Scand J Work Environ Health 1987;
13:118-23. 26. Heppleston AG. Silica. pneumoconiosis. and carcinoma of the lung. Am J
Ind Med 1985: 7~285-94. 27. Goldsmith DF. Guidotti TL. Johnston DR. Does occupational exposure to
silica cause lung cancer? Am J lnd Med 1982: 3:423-40.
28. Lugano EM. Dauber JH.Elias JA. Bashcy R1. Jimenez SA. Daniele RF'.
The regulation of lung fibroblast pmliferation by alveolar macrophages in expenmental silicosis. Am Rev Respir Dis 1984: 129767-71. .29. Schmidt JA. Oliver CN, Lepe-ZunigaJL. Green 1. Gery I. Silica-stimulated monocytes release fibroblastproliferation factors identical to interleukin 1: a potential role for interleukin I in the pathogenesis of silicosis. J Clin Invest 19x4: 73:1462-72. 30 Yu XF. Zou CQ. Lin ME. Observations of the effect of tetrandrine on expenmental silicosis use of rats. Ecotoxicol Environ Safety 1983: 7306-
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THE NEW ENGLAND JOURNAL OF .MEDICINE
M a r c h I . 19%
* 3 I . Goldstein B. Rendall RE. The prophylactic use of polyvinylpyridine-Noxide (PVNO) in baboons exposed to quartz dust. Environ Res 1987 42:469-8 I .
32. Venables KM. Epidemiology and [he prevention of occupational asthma. Br J Ind Med 19x7: 44:73-5.
33. Axelsson IC. Johansson SG. Zetterstrom 0. Occupational allergy to weeping rig in plant keepers. Allergy 1987: 42161-7.
34. Maestrelli P. Marcer G. Dal-VecchioL. Occupational asthmadue to ebony wood (Diospyros crassiflora) dust. Ann Allergy 1987; 59347-9.
35. Hinojosa M. Losada E. Moneo I, Dominiguez J. CYTilloT. Sanchez-Cano M. Occupational asthma caused by African maple (Obeche) and Ramin: evidence of cross-reactivity betwen these two woods. Clin Allergy 1986 I 6 145-53.
36. Henderson AK. Ranger AF. Lloyd J. McShany C. Mills RJ. Moran F.
Pulmonary hypersensitivity in [he alginate industry. Scon Med J 1984; 29%-5.
37. Smith AB. Bernstein DI. Aw TC. et al. Occupational asthma from inhaled egg protein. Am J Ind Med 1987: 12:205-18.
38. Ostrom NK. Swanson MC. Agarwal MK. Yunginger JW. Occupational allergy to honeybee-bodydust in a honey-processing plant. J Allergy Clin Immunol 1986: 77:73640.
39. Resta 0, Foschino-Barbaro MP, Camimeo N. Di-Napoli PL. Pavese 1, Schino P. Occupational asthma from fish-fed Echinodorus plasmosus larva. Med Lav 1982; 73234-6.
40. Lutsky 1. Teichtahl H. Bar-Sela S . Occupational asthma due to poultry mites. J Allergy Clin lmmunol 1984: 7356-60.
4 I . Gold BL. Mathews KP. Burge HA. Occupational asthma caused by sewer flies. Am Rev Respir Dis 1985: 13199-52.
42. Cartier A. Malo JL. Dolovich J. Occupational asthma in nurses handling psyllium. Clin Allergy 1987: 17:l-6.
43. Moscato G. Naldi L, Candera F. Bronchial asthma due 10 spiramycin and adipic acid. Clin Allergy 1984: 14:355-61.
44. Asai S. Shimoda T. Hara K. Fujiwara K. Occupational asthma caused by isonicotinic acid hydratine (INH) inhalation. J Allergy Clin lmmunol 1987; 50578-82.
45. Malo JL. Pineau L. Cartier A. Occupational asthma due to azobisformamide. Clin Allergy 1985: 152614.
46. Lozewicz S, Davison AG. Hopkirk A, et al. Occupational asthma due to methyl methacrylate and cyanoacrylates. Thorax 1985: 405436-9.
47. Moscato G. Biscaldi G. Cottica D. P u g l i e F, Candura S, Candura F. Occupational asthma due to styrene: two c a re~ports. J Occup Med 1987: 29957-60.
48. Malo JL, Cartier A. Occupational asthma due to fumes of galvanized metal. Chest 1987: 92:375-7.
49. Chan-Yeung M. Lam S. Occupational asthma. Am Rev Respir Dis 1986 133:686-703.
50. McGrath KG. Zeiss CR. Patterson R. Allergic reactions to industrial chemicals. Clin lmmunol Rev 1983; 2:l-58.
51. Chan-Yeung M. Occupational asthma. Clin Rev Allergy 19864251-66. 52. Block G. Tse KS. Kijek K. Chan H. Chan-Yeung M. Baker's asthma:
clinical and immunologic studies. Clin Allergy 1983; 13:359-790. 53. Chan-Yeung M. Immunologic and nonimmuwlogic mechanism in asth-
ma due to western red cedar (Thuja plicara). J Allergy Clin Immunol 1982; 70:32-7. 54. Tse KS. Johnson A. Chan H. Chan-Yeung M. A study of serum antibody
, activity in workers with occupational exposure to diphenylmethane diisocyanate. Allergy 1985; 40314-20.
55. Malo JL. Cartier A. Gagnon G. Evans S. Dolovich I . Isolated late asthmatic reaction due to nickel sulphate without antibodies to nickel. Clin Allergy 1985; 1595-9.
56. Saric M. Godnic-Cvar J. Gomzi M. Stilinovic L. The role of atopy in potroom workers' asthma. Am J Ind Med 1986 923942.
57. Brooks SM. Weiss MA. Bernstein IL. Reactive airways dysfunction syndrome (RADS): persistent asthma syndrome after high level irritant exposures. Chest 1985; 88:376-84.
58. Pepys J. HutchcroR BJ. Bronchial provocation tests in etiologic diagnosis and analysis of asthma. Am Rev Respir Dis 1975: 112829-59.
59. Hendrick DJ. Bronchopulmonary disease in the workplace: challenge testing with occupational agents. Ann Allergy 1983: 51:179-84.
60. Hargreave FE. Dolovich J. Boulet L-P. Inhalation provocation tests. Semin Respir Med 1983; 4224-35.
61. Cockcroft DW. Bronchial inhalation tests. 11. Measurement of allergic and occupational bronchial responsiveness. Ann Allergy 1987: 598998.
62. Moller DR. Brooks SM. McKay RT. Cassedy K. Kopp S. Bernstein IL. Chronic asthma due to toluene diisocyanate. Chest 1986: W.494-9.
63. Mapp CE. Corona PC. De Marzo N. Fabbri L. Persistent asthma due to
isocyanates. Am Rev Respir Dis 1988; 137:1326-9.
64. Chan-Yeung M. Lam S . Koener S.Clinical features and natural histoty of
occupational asthma due to Western red cedar (Thuja plicata). Am J Med 1982; 72:411-5.
65. Burge PS. Occupational asthma in electronics workers caused bv colophony fumes: follow-up of affected workers. Thorax 1982: 37:34& 53.
66. Malo JL. Cmier A . Ghezzo H. LaFrance M. YcCants M. Lehm S B , Patterns of improvemenr in spirometry. bronchial hypemponsivenes. and specific IgE antibody levels after cessation of exposure in occupational asthma caused by snow-crab processing. Am Rev Respir Dis !988: I38:807- 12.
67. Cornier Y. Belanger J. &Blanc P. Laviolene M. Bronchdveolar lavage
in farmers' lung disease: diagnostic and physiologic signilicance. Br J Ind Med 1986 43:401-5.
68. Leatheman JW. Michael AF. Schwam BA. Hoidal JR. Lung T-cells In hypersensitivity pneumonitis. Ann Intern Med 1984. 100:390-2.
69: Calvanico NJ. Ambegaonkar SP. Schluetcr DP. Fink JN. Immunogl&uiin levels in bronchoalveolar lavage fluid from pigeon breeders. J Lab Clin
Med 1980. %.129-40.
70. Zeiss CR. Kanellakes TM. Bellone ID. k V i Q D. Pruzansky JJ. Patternn R. Immunoglobulin E-mediated asthma and hypersensitivity pntumonitis with precipitating anti-hapten antibodies due to diphenylmethane di-
isocyanate (MDI) exposure. J Allergy Clin lmmunol 1980 65% 52. 7 I . Malo JL. Zeiss CR. Occupational hypersensitivity pneumonitisafter exposure to diphenylmethane diisocyanate. Am Rev Respir Dis 1982; 125:113. 6.
72. Yoshizawa Y, Ohtsuka M.Noguchi K. Uchida Y.Suko M. Hasegawa S.
Hypersensitivitypneumonitis induced by toluene diisocyanate: sequelaeof
continuous exposure. Ann Intern Med 1989: 11031-4. 73. Patterson R. Zeiss CR. Pntzansky JJ. lmmunology and immunopathology
of trimellitic anhydride pulmonary reactions. J Allergy Clin lmmunol
1982; 7019-23. 74. Rylander R. Schilling RS. Pickering CA. Rooke GB. Dempscy AN, Ja-
cobs RR. Effects after acute and chronic exposure to conon dust: the Manchester criteria. Br J Ind Med 1987: 44577-9. 75. Beck GJ. Maunder LR. Schachter EN. Cotton dust and smoking effects on lung function in cotton textile workers. Am J Epidemiol 1984, 11933-
43. 76. Beck GJ. Schachter EN. Maunder LR, Schilling RS. A prospective study
of chronic lung disease in cotton textile workers. Ann Intern Med 1982; 97645-5 1. 77. Merchant JA. Lumsden JK. Kilbum KH, et al. An industrial study of the biologic effects of cotton dust and c i g m n e smoke exposure. J Occup Med 1973: 15:212-21. 78. Ran PC,Vollmer RT. Miller JA. Epidemiology of pulmonary lesions in nontextile and cotton textile worken: a rerrospective autopsy analysis.
Arch Environ Health 1980 35133-8. 79. Milton DK. Chawla XK. Cotton dust contains proteolytic and elastolytic
enzymes not inhibited by alpha-I-proteinase inhibitor. Am J Ind Med 1986: 9~247-60. 80. Haglind P. Rylander R. Exposure to conon dust in an experimental cardroom. Br J Ind Med 1984: 41:340-5. 81. Rylander R. Bacterial toxins and etiology of byssinosis. Chest 1981; 79Suppl:34s-38S. 82. Castellan RM, Olenchak SA. Kinsley KB. Hankinson JL. Inhaled endotoxin and decreased spiromettic values: an exposu-sponse dation for cotton dust. N Engl J Med 1987; 317:605-10. 83. Kennedy SM. Chnstiani DC, Eisen EA. et al. Cotton dust and endotoxin
exposure-response relationships in conon textile workers. Am Rev Respir Dis 1987: 135:194-200.
84. Douglas JS. Duncan ffi. Zuskin E. Characterization of textile dust
extracts. 11. Bronchoconstriction in man. Br J Ind Med 1984, 41:7& 6. 85. Eisenbud M. Origins of the standards for conml of beryllium di-
(1947-1949). Environ Res 1982; 27:79-88. 86. Eisenbud M, Lisson J. Epidemiologic aspects of beryllium-indWd.
nonmalignant lung disease: a 30 year update. J ofcup Med 1983: =I%202. 87. Cullen MR. Kominsky JR, Rossman MD, et al. Chronic beryllium d i y
in a precious metal refinery: clinical epidemiologic and immunologk eVidence for continuing risk from exposure to low level beryllium fume. Am
-Rev Respir Dis 1987; 135:201-8.
88. Beryllium disease among workers in a spacecraft-manufacturingplant California. MMWR 1983; 32:419-20. 425.
89. Epstein PE. Dauber IH. Rossman MD. Danick RP. BronchdvWlN I*vage in a patient with chronic berylliosis: evidence for hypeMnSitivity pneumonitis. Ann Intern Med 1982: 97:213-6.
90. Rossman MD. Kern JA. Elias JA. et al. Proliferative mponse Of bmnchoalveolar lymphocytes to beryllium: a tesr for chronic beryllium disc*.
Ann Intern Med 1988: 108:687-93. 91. Lauwerys RR. Bernard A. Early detection of the nephrotoxic effmOf
industrial chemicals: state of the art and future prospects. Am J Ind Med
1987: I1:275-85.
\lo\. 322 NO.9
OCCUPATIONAL MEDICINE -CULLEN ET AL.
601
92. Cullen MR. Robins JM. Eskenazi B. Adult inorganic lead intoxication: presentation of 3 I new cases and a review of recent advances in the literaNE. Medicine 1983: 62:221-47.
93. Batuman V. Landy E. Maesaka JK, Wedeen RP. Contribution of lead to hypefieension with renal impaimxnt. N Engl J Med 1983; 309:17-21.
94. Batuman V. Maesaka JK. Haddad B. Tepper E. h d y E. Wedcen RP. The
role of lead in gout nephropathy. N Engl J Med 1981; 3W520.3.
95. Lauwerys R. Bernard A. Viau C. Buchet JP. Kidney disorderspndhematotoxicity from organic solvent exposure. S a n d J Work Environ Health 1985; I I:S~ppl1:83-90.
%. Churchill DN. Fine A, Gault MH. Association bet- hydrourbon e x p sure and glomerulonephritis: an a p p s a l of the evidence. Ncphmn 1983: 3 3 169-72.
97. Daniel1 WE. Cower WG. Rosenstock L. Occupational solvent exposure and glomloncphritis: a csse repon and review of the literatwe. JAMA 1988: 2592280-3.
98. Beirne GJ. Brennan JT.Glomerulonephritis associated with hybourbon solvents: mediated by antiglomerular basement membrane antibody. A d Envimn Health 1972; 25:365-9.
99. Kleinknecht D. Morel-Muoger L. Callard P. Adhcmv JP. Mahieu P. Antiglomuular baument membrane nephritis a k r solvent exposure.Amh lntern Med 1980: 140:230-2.
I@). Sprecact GA. Idiopathic pulmonary hemosiderosis: pe-l experience with six adults treated within a ten-month period. and a review of the literature. Am Rev Respir Dis 1%3; W.3XI-7.
101. Hcale WF, Matrhiesson AM, Niall JF. Lung hamorhagc and nephritis (Goodpasture's syndrome). Med J Aust 1%9; 2355-7.
102. KIavis G.Drummer W. Goodpasnuesyndrome and the effects of knzcnc. Axh Toxikol 1970 26:40-55.
103. Saliger K. Huland H. Kasuistischer beitrag wr atiologie des Goodpasturesyndromes. Mal Klin 1973: 68:437-40.
104. Nathan AW. ToMiand PA. Goodpasture's syndrome and mchlomethanc intoxication, Br J Clin Pharmacol 1979; 8284-6.
105. Carlier B. Schrader E. Mahieu P. A rapidly and sponwewsly rewrsible GoodpasNre's syndrome after carbon teaschloride inhalation. Acta C l i Bel% 1980 35:193-8.
106. Keogh AM. Ikls LS,Allen DH. Isbister JP. Kennedy MC. Exacehation of Goodpasture's syndrome after i n d v c m n t exposure to hydrourbon fumes. Br Med J 1984: 288:188.
107. Franchini I. Cavatorta A. Falzoi M. LUceKini S. Muni A. Early indicators of renal damage in workers exposed to organic solvents. lnt Arch Occup Envimn Health 1983; 521-9.
108. Askergen A. Organic solvents and kidney function. In: Englund A,
Ringen K. Mehlman MA. eds. Occupational health hazards of solvents. Princeton. N.J.: Princeton Scientific Publishers. 1982157-72. 109. Viau C. Bernard A. Lauwerys R. et al. A cross-sectional survey of kidney
function in refinery employees. Am J Ind Med 1987: ll:I77-87. 110. Sapin C. Druet E. Druet P. Induction of anti-glomerular basement mem-
brane antibodies in the Brown-Noway rat by mercunc chloride. CIin Exp ~mmunol1977: 28:173-9. 111. Roman-FrancoAA.TurielloM. AlbiniB.OssiE.MilgromF.AndmGA.
Anti-basement membrane antibodies and antigen-antibody complexes in rabbits injected with mercuric chloride. Clin lmmunol lmmunopathol 1978: 9464-81.
112. Dunn TB. Morris HP. Wagner BP. Lipemia and glomerular lesions in nts fed diets containing N-N'discetyl- and 4 . 4 4 ' . 4 ' - t e m m c t h y l b i n e . Roc Soc Exp Biol Med 1956: 91:105-7.
113. Bremner DA, Tange JD. Renal and neoplastic lesions after injection of Nnldiacetylbcnzidine. Arch Rthol 1966; 81:146-51.
114. Harman JW. Chmnic glomuulonephritis and the nephrotic syndrome induced in rats with N.N'diacaylknzidinc. J Rthol 1971; 104:119-28.
115. Zimmennan SW. Nohach DH. Nephrotic effects of long-term carbon tetrachloride administration in rats. Arch Path01 Lab Med 1980; IW%-9.
116. FPrley JR. Holland JM. Gipson LC,Whitaker MI. R e d toxicity of middle distillates of shale oil and permleum in mice.Toxicol Appl phumrol
1982: 65%-91. 117. Roscnstak L. Cullen MR. Clinical occupational medicine. Phildelphii
W.B. Saunders. 198644-57. 118. Cronkite EP. Chemical leukemogenesis: benzene as a modcl. Semin He-
mtol 1987; 24:2-1 I . 119. Aksoy M. M e m S.DinCol C . Leukemia in shoe workers exposcd h i -
cally to benzene. Blood 1974.44%3741. 120. D e h P. Borgomano C. Leukemia aiguc an cours de I'intoxication ben-
zcnique. sur I'origine toxique de ccrcains leukemics arguesen leur relations avec les anemies prrves. J Med Lyon 1928; 9227-33. 121. Maltoni C. Conti B. Cotti G.BeIpoggi F. Experimental studies on benzene
carcinogenicity at the Bologna Institute of Oncology: c m t resulu and ongoing mearch. Am J Ind Med 1985; 7 : 4 1 5 4 .
122. Snyder CA, Goldstcin BD,Scllakumu AR. A l k R~E. Evidcncc for hc-
matotoxicity and Nmoripmsis in rats exposcd to 100ppm benttnc. Am J Ind Med 1984: 5429-34.
123. Kalf GF. Snyder R. Rushmore TH. Inhibition of RNA synthesis by knzcne metabolites and their covalent binding to DNA in rabbit bone marrow
mitochondria in v i m . Am J Ind Mcd 1985; 7485-92. 124. Cronkite EP. Drew RT. lnoue T. Bullis JE. &Nene hemtotoxicity uid ..
leukemogenesis. Am J Ind Med 1985; 2447-56.
-125. Aksoy M. Benzene as a leukemogenic and carcinogenic agent. Am J Ind Med 1985: 89-20. 126. Rinsky RA. Smith AB, HwMlng R, et al. Bcnzcnc and Ieukmip: an
epidemiologic risk assessment. N Engl J Med 1987: 3161044-50. 127. Nagano K, Nakayama E, Oobryashi H, et al. Embryotoxic c f f s a of
ethylene glycol monomethyl ether in mice. Toxicology 1981: m335-43.
128. Miller RR. A y e s JA. cllhoun LL,Young JT. McKmna MI. Complntive
shon-term inhalation toxicity of ethylene glycol monomethyl ether a d
propylene glycol monomethyl ether in rats and mice. Toxicol Appl Pharmacol 1981; 61:368-77.
129. Ohi G.Wegman DH. Tranxutaneous ethylene glycol monomethyl ether poisoning in the work semng. J Occup Med 1978; 20675-6.
130. Cohen R. Reversible subacute ethylene glycol monomethyl ether toxicity associated with microfilm production: a case repon. Am J Ind Med 1984;
6441-6.
131. Cullen MR. Rad0 T. Waldron JA. Sparer J. Welch LS. Bone n w m w
injury in lithographers exposed to glycol ethers and organic solvents used in multicolor offset and ultraviolet curing printing processes. Arch Envimn Health 1983: 38347-54.
132. Welch LS. Cullen MR. Effect of exposure to ethylene glycol e t k o~n
shipyard painters. 111. Hematologic effects. Am J Ind Med 1988; 14527-
36.
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-OCCUPATIONAL MEDICINE CULLEN ET AL.
MEDICAL PROGRESS
OCCUPATIONAL MEDICINE (Second of Two Parts)
MARK R. CULLENM, .D., MARTIN G. CHERNIACK, M.D., AND LINDA ROSENSTOCK, M.D., M.P.H.
675
Neurologic Disorders
The tendency of certain workplace toxins, including organic solvents such as n-hexane, metals such as lead and arsenic, and certain organophosphate compounds, to cause profound and occasionally irreversible damage to the axons of peripheral nerves has been known for several decades.`33The irreversible central nervous system effects of related compounds have also been well characterized in defined settings: the organic psychosis caused by the solvent carbon disulfide, the diffuse encephalopathy observed in glue sniffersexposed to toluene, and the devastating consequences of lead intoxication in children, for exam-
le.'^"^^ In the past several years a new and far more
serious question has been raised: does repeated exposure to legally acceptable and widely occurring levels of these kinds of compounds result in chronic neurologic dysfunction, especially of the central nervous system?
The impetus to examine this possibility has come from two directions. In the late 1970s two Scandinavian case-control studies found a disproportionate number of workers who had been exposed to organic solvents among groups of men who had retired pre-
maturely because of neuropsychiatric problem^.'^^*'^^
During` the same period, the nature of dementia among elderly people in developed countries was characterized with increasing evidence that mental deterioration was not an obligatory physiologic consequence of aging, but a pathologic disturbance. Given the realities of the ubiquitous use of solvents in the workplace and an increasingly aged population, the clinical and public health implications of an effect are considerable.
Unfortunately, almost a decade of prodigious effort has not yielded clear answers about the pattern and went of solvent-induced neurologic dysfunction. Relying heavily on the clinical interpretation of batteries [Jf neuropsychological tests, Scandinavian investiga-
have defined a "psychoorganic syndrome" characterized by fatigue, memory loss, difficulty in concen.[ration,and emotional lability after 5 to 10years of the `eKular use of solvents such as styrene and toluene in rroups of painters. metal degreasers, plastics workers, dnd chemical workers. "q Although compensable in
the Yale-New Haven Occupational Medicine R0.m. Yale University xhmlof Medicine. New Haven. Conn. (M.R.C., M.G.C.). and the Occupaywd Medicine Ragram. Unlversiry of Washrngton School of Medicine. Seattle L.R.J. Addms repnnt requests io Dr. Cullen at the Occupational Medicine
333 Cedar SL. New Haven. (3`06510
Sweden, Finland, and Denmark, reproducible abnormalities have not been found consistently on routine tests such as neurologic examination, electrophysiologic studies, or r a d i ~ g r a p h y . ' ~ ,L'o~n'gitudinal studies of workers removed from exposure have shown that the disorder is generally stable, with some regression of symptoms in milder cases and only rare progression, making the syndrome clearly distinct from the broader group of disorders involving dementia, especially Alzheimer's d i s e a ~ e . ' ~ ~ * ' ~ ~
Studies and clinical observations in the United Kingdom and North America have been far less consistent. Although new tools, such as computerized batteries of neuropsychological tests, have been developed to facilitate epidemiologic study,'& only the tendency toward poorer test results in workers with longer and heavier exposure has been proved. Clinically meaningful sequelae have not been seen with the frequency that the Scandinavian experience would predict.'45J46Studies among patients with Alzheimer's disease have failed to identify exposure to organic solvents as an associated risk.I4' Moreover, neither human neuropathological observations nor data from experiments in animals have provided confirmatory evidence. 148
Putting all the discrepant facts together, it seems most prudent to presume that repeated and heavy exposure to solvents can lead to chronic neuropsychological dysfunction, which may become irreversible in patients who are not removed from exposure soon after the onset of symptoms. In patients who are removed from exposure, the prognosis appears favorable. O n the other hand, it seems unlikely on the basis of available data that much of the Alzheimer's disease epidemic can be attributed to organic solvents. The contributory role of solvents and other occupational or environmental contaminants, such as aluminum, 149.150 should not be excluded from further investigation, however, until the pathogenesis of this devastating disorder is fully understood.
Gastrointestinal Disorders
Although early investigations of the effects of carbon tetrachloride on hepatic structure and function became a classic model for the study of occupational disease, there has been surprisingly little recent interest in the role of occupational factors in the pathogenesis of liver or gastrointestinal diseases. 15' A few recent reports suggest that toxic hepatitis or, more accurately, hepatic injury (since inflammatory cells
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THE NEW ENGLAND JOURNAL OF MEDICINE
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may not be part of the histologic appearance) may occur more frequently than is assumed. perhaps masquerading as alcohol-, drug-, or virus-related illness. Three well-documented outbreaks in developed countries have been reported since 1982, related to the epoxy hardener methylenedianiline (the cause of Epping jaundice), the solvent dimethvlformamide, and a
chemical mixture. i52-i54 In each outbreak, a number of cases occurred under normal operating conditions in textile coating, chemical production, and plastic manufacturing. The differing clinical patterns of disease in the outbreaks are also disconcerting: methylenedianiline caused rapidly resolving cholestasis, whereas dimethylformamide and the chemical mixture were associated with hepatocellular injury and widely varying recovery periods. Although a tendency toward clinical improvement was described in each cluster, longitudinal follow-up was insufficient to exclude late sequelae, especially chronic hepatitis or cirrhosis, whose relation to toxic exposures remains unelucidated. Reviewers have stressed the fortuitous circumstances that led to the recognition of these outbreaks, emphasizing the need for diagnostic vigor when seronegative hepatic abnormalities develop in workers exposed to chemicals.
Endocrine and Reproductive Effects
Despite a growing public perception that toxic exposures may be responsible for infertility, spontaneous abortion, and birth defects, accumulated knowledge about adverse effects in humans remains extremely limited; adequate information exists for only a handful of agents. Male infertility, in theory the easiest outcome to study because the entire physiologic pathway converges into a single, readily quantifiable body fluid, has in practice been difficult to evaluate because many workers find testing unacceptable, and specimens require immediate analysis.L56Fortunately, animal sperm have been a reasonable substitute. Adverse effects in women, both before and after conception, are harder to study. Infertility cannot be diagnosed by any simple clinical test, birth defects are generally too rare and heterogeneous for causal analysis, and spontaneous abortions are very common but are usually undetected, 157 rendering studies in large populations highly susceptible to recall bias. -Moreover, the differences between the physiology of women and that of nonprimate mammals make extrapolation from experimental models highly speculative.
These limitations notwithstanding, some credible associations have emerged in the past several years. Starting with the highly publicized discovery of epidemic oligospermia and azoospermia among chemical workers producing the pesticide dibromochloropro-
pane, studies have demonstrated depressed sperm counts related to exposure to lead and the solvent carbon disulfide.i5y-lbFior a variety of other solvents (ethylene glycol ethers, for example), pesticides (such as ethylene dibromide), metals (such as mercury and ar-
senic), and alkylating agents (ethylene oxide. tor example), data from studies in animals predict the
likelihood of human spermatotoxic effects.i2i.I'L-'h+
In-
terestingly, data suggest that the disruption o t the
relevant endocrine tunction - hypothalamic. pitu-
itary, or testicular -may be the primary or associated
affected pathwav in some instance^.^^^.^^' This was evi-
dently the mechanism in a recently reported case of
infertility in an embalmer exposed to a chemically
complex massage cream with estrogenic activity.166
As noted, the data base on female workers is more
precarious. Excesses in the reported rates of spontane-
ous abortion or perinatal death have been described
in many occupational settings: among medical and
dental workers exposed to anesthetic gases, eth-
ylene oxide, or viral agentsia; lead workersL69;
rubber workers exposed to organic s o l ~ e n t s lw~o~rk; -
ers producing s e m i c o n d ~ c t o r s ~an~d~ ;women doing
heavy labor.L72Biologically plausible hypotheses exist
for each outcome, and they are corroborated by the
results of experiments in animals that, although of
questionable predictive value, are sufficient to suggest
that job modification or transfer is a reasonable pre-
scription for pregnant workers until more data are
available. For those exposed to excessive amounts of
lead, the metal's documented transplacental deposi-
tion, combined with its known adverse developmental
impact in infants, probably justifies an aggressive
stance. Removing from exposure women who are con-
templating future pregnancy may also be reasonable,
because of lead's long skeletal storage and potential
mobilization by pregnancy or 1actati0n.l~R~emoval
also seems reasonable for those exposed to ionizing
radiation or organic mercury, the only documented
nonpharmaceutical occupational teratogens in hu-
m a n ~ a,nd~ f~or~those exposed in the workplace to
pharmaceuticals of proven teratogenicity, such as es-
trogenic or cytotoxic agents. A recent unexpected find-
ing may also have clinical ramifications. In a prospec-
tive study of over 4000 consecutive pregnancies,
maternal exposure to organic solvents was a strong
predictor of preeclampsia and other hypertensive dis-
~rders,~~'outcomtheast put both the mother and fetus
at risk.
Given the importance of reproductive health in an
era in which the majority of women work outside the
home, the most exciting new contribution to the field
has been the development and field testing by WilCOX
and colleagues of a new and simple method of ascer-
taining pregnancy and fetal loss early and v i r t d Y
us-completely in women followed up pro~pectively.'~~
ing daily urine collections and a highly specific imm'-
noradiometric assay for the beta chain of human cbo-
rionic gonadotropin that is sensitive enough to detect
pregnancy soon after implantation, the method should make true rates of pregnancy and early fetal loss readily measurable in women exposed to agents of Con-
-cern. Since losses are frequent - 31 percent of a"
pregnancies in an early trial of the methodi5' it
vol. 322 NO. 10
-OCCUPATIONAL MEDICINE CULLEN E T AL.
677
should be possible to expand the human data base from further clinical observations of affected popula-
quickly in the coming decade through the study of tions. Documenting that these workers often have a
relatively small groups.
diffuse constellation of shoulder, arm, and hand prob-
Musculoskeletal Disorders
lems, including pain and numbness, investigators, largely from Scandinavia, have coined the concept of
Even after the consequences of accidental injuries the hand-arm vibration ~yndrome.'~P'atients may
are excluded, acute and chronic disorders of the trunk present with features suggestive of cervical, ulnar, or
and extremities remain extraordinarily frequent median-nerve entrapments, with or without overt
causes of morbidity and consequent lost work time digital vaso~pasm.'A~'lthough the results of tradition-
and productivity. Although an occupational basis for al electrophysiologic tests have been inconsistent,'*
many common problems, such as low back pain and an overlap with abnormalities more typical of isolated
degenerative arthritis, remains far from clear, 175 recent nerve entrapment may be seen, complicating differen-
epidemiologic studies have implicated occupational tial diagnosis." This finding is compatible with data
factors in the carpal tunnel syndrome,17618a2common from experiments that demonstrate comparable neu-
example of the so-called cumulative-trauma dis- ropathic consequences from pressure and vibraorders. Using quantified biomechanical measures and tion. 187,195
videotaped documentation of work practice, ssudies
Although a definitive strategy for the evaluation
have shown that force, repetition, and vibration are and treatment of such patients awaits further investi-
the most relevant occupational risks for this common gation, certain clear implications have emerged. For
condition.176,182-184Experimental models that use such those with evident vasospasm, permanent removal
extrinsic stressors have begun to cast doubt on the from exposure to vibration is probably unavoidable, in
pathophysiologic axiom involving the compression of view of the mounting evidence that vascular changes
the median nerve at the wrist. New data suggest the are reversible only slowly if at all and that reversibility
possible primary involvement of glabrous skin recep- is related to the duration of exposure once symptoms
tors and other distal small nerves due to edema of the are present. Calcium-channel blockers benefit some
nerve sheaths inducible by pressure or
patients, as in Raynaud's phenomenon due to other
The complexity of such a mechanism, involving large causes. In the absence of vascular symptoms, conser-
and small nerves, may explain why standard clinical vative approaches, including temporary removal from
and electrodiagnostic tests often fail to explain symp- the job, splinting, and antiinflammatory regimens,
toms188or predict the clinical course or response to may suffice, although objective therapeutic end points
surgery.189,190
may be lacking. Surgical interventions, such as release
At the practical level, the data are sufficiently clear from entrapment, should be reserved for rare cases
to add a careful review of work activities to the diag- with clear-cut neural abnormalities in which medical
nostic evaluation of every patient, irrespective of other thrrapy has failed.
personal risk factors or conditions. This is best accomplished by having the patient demonstrate work activ- Cancer
ities. For those such as assembly-line workers, materi-
The success of epidemiologists in the 1960s and
als handlers, grinders, mechanics, and even clerical 1970s in establishing the excess cancer risk for workers
workers who are exposed to forceful, repetitive, or exposed to several widespread workplace agents, most
awkward wrist motions or vibrating tools, a trial of notably asbestos, benzene, and benzidine dyes, raised
removal from exposure may be appropriate, whether the possibility that cancer overall might largely be
Or not the results of standard diagnostic tests are de- attributable to exposure in the workplace. Ecologic
finitive.Surgery should probably be reserved for cases data showed some congruity between regions with
involving evident weakness or atrophy and those that high rates of cancer and high levels of industrial activ-
fail to respond to conservative management. Where ity, and an unpublished government document pur-
multiple cases have occurred, interventions to modify porting to show that 20 to 38 percent of all cancers
the way work is done are certainly warranted.
were attributable to workplace exposures received cir-
Vibrating hand-held tools may also cause severe culation and attention. The past decade has witnessed
hand dysfunction. The vibration white finger syn- a considerable sobering and refinement of the prevail-
drome involves a vascular spasm induced by cold that ing views. Although over 300 compounds have been
may be difficult to differentiate from Ravnaud's phe- shown to have carcinogenic potential on the basis of
nomenon. Recent plethvsmographic studies have doc- their effects in laboratory animals, no new class of
umented temperature-sensitive changes in digital- compounds has been added to the list of previously
blood flow. even in asvmptomatic grinders. sawvers. established human carcinogens (Table 2). Newer esti-
hkhammerers. and others with heavv e x p o ~ u r e . ' ~ ' ~m' ~at~es of the total influence of workplace exposure on
The use of pharmacologic blocking agents has sug- the US.cancer rate have ranged from 4 to 10 per-
gested both central and local sympathetic dvsfunc- cent,209.2 IU
tion.''''These physiologic effects notwithstanding, the
Despite this reduced estimate, important contribu-
most notable advances in the past decade have come tions relevant to clinical practice are emerging. First,
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678 THE NEW ENGLAND JOURNAL OF MEDICINE
Table 2. Established Causes of Cancer from Workplace Exposure.
AGENT
Para-aminodiphenyl Asbestos
Arsenic Alkylatingagents(mahlonchamim hydro-
chloride and bis[chloromethyll ether)
Benzcne
Benzidine, beta-naphthylamine. and derived dyes
Chromium and chromatcs Ionizing radiation
Gamma rays
Radon Radium
.>-'
Nickel
Polynwleac a m d c hydrocarbons (fromcoke. coal tar. shale, mineral oils. and cnosotc)
Vinyl chloride monomer
Wood dust
Chemical manufacturing Consmcaon, asbestos rmning
and milling. pmducaon of fricaon products and cement Copper mining and smelting Chemical manufacturing
Chemical and rubber manufacmring. pemleum refining
Dye and textile production
Tanning. pigment making
Nuclear. health care
Uranium and hematite mining Watch painting Nickel refining Steel making. roofing,
chimney cleaning
Chemical manufacturing Cabinetmaking. carpentry
Urinary bladder Pleura, pentoncum. bronchus
Skin. bronchus. liver Bronchus
Bone marrow
Urinary bladder
Nasal sinus. bronchus
Skin, thyroid, bronchus, bone marrow
Bronchus Bone Nasal sinus, bronchus Skin. SCroNm, bronchus
Liver Nasal sinus
Melick et d.'* Mossman and Gee"
Pinto et d.19* Rgueroa et al.'*
Rinsky et ai.'%
case et al.m
Hayes"'
National Research Council zoz National Research Cwncil"' Polednak et d.ly Grandjean et ai.'Hammond et aI.'06
Waxweiler et ai.*m Acheson et aL201
there has been progress in elucidating the effects of
relatively low doses of exposure to the established carcinogens in order to modulate predictions that are based on experience with very high doses in humans or on extrapolation from studies in animals. Since millions of workers are still exposed to small amounts of agents such as nickel and chromium (in
welding and toolmaking, for example), polynuclear
aromatic hydrocarbons (in mineral oils and vehicle
exhaust),benzene (in gasoline and solvent mixtures),
and ionizing radiation, such data are crucial in protecting or reassuring patients. Although polemicists have generally argued that low doses should be classified as either unquestionably safe or generically unacceptable, the accumulating data suggest that experience is mixed. The work of Rinsky et aLiZ6suggests that the leukemogenic effects of low levels of benzene are sufficient to dictate a strong effort to eliminate exposure to this agent wherever feasible. Published studies of nuclear-defense workers suggest that achievable low levels of alpha and gamma radiation may be associated with small but measurable increases in the risks of lung cancer and although more dire interpretations have been offered.213On the other hand, data have not demon-
strated measurable cancer risks in industries - such
as grinding or plating -that use nickeLZo5Chromium
in the steel alloys most often encountered in the workplace has not been proved carcinogenic, although chromic acid used in plating operations and pigments and tanning solutions that contain chromate are a
p r ~ b l e m . ~T~h' e~ p"o~ssibility that oil mists cause excess lung and gastrointestinal cancer at levels commonly encountered in the workplace has been suggest-
ed but not proved; excess skin and scrotal cancer does
occur in exposed
Diesel exhaust appears to
be carcinogenic, and small increases in lung cancer
have been noted among bus and truck drivers and
me~hanics.~'~**''
Second, estimates of the risk to humans for some of
the more widely used suspected carcinogens (suspect-
ed largely because of their effects in animals) have
been developed. The most important suspects are list-
ed in Table 3, along with common sources of occupa-
tional exposure. Although there is no definitive evi-
dence against any of the suspected carcinogens, the
studies cited provide clues to effects in humans and in
some cases delineate target sites for future investiga-
tions. Serious debate continues over each agent, with
potentially important legal and regulatory ramifica-
tions, but sufficient data already exist to allow some
broad generalizations to guide clinical and public
health practice. On the one hand, none of these com-
mon substances can be exonerated of the potential to
cause cancer in humans, and this has led in virtually
every case to strong recommendations for changes or
actual regulatory changes lowering the acceptable
limits of exposure in the United States. O n the other
hand, a review of the upper confidence limits of the
risk estimates (the worst-case prediction) shows that
none of these agents, with the possible exception of
ethylene oxide, will cause the markedly altered can-
cer risks typical of the confirmed carcinogens listed
in Table 2. Relative-risk estimates have generally
ranged between 1 (normal background risk) and 2
(doubled risk). Since most studies were conducted in
populations exposed to relatively high, often uncon-
trolled levels of the agents, clinicians can safely take
r I-
vol. 322 NO. 10
AGE"
&lyllium
Cadmium mylene oxide Formaldehyde Synthetic mineral fik~
(e& fibrous glass) polychlorinated biphenyls Organochlorine pesticides
(e.g., chlordane, dieldrin) Silica
OCCUPATIONAL MEDlCINE -CULLEN E T AL.
Table 3. Widely Used Suspected Human Carcinogens.
INWSTUES AND TRADE5
Beryllium processing, aimaft maIIUfaCNnng, electronics, secondary smelting
Smelting, bancry making, welding
Hospitals, produdon of hospital supplies
Plastic, textile, and chemical pFoduction; health can
Manufacturing. insulation
Elcckical-cquipmmt production and maintenance
Pesticide manufaam and application, agriculture
Casting. mining, refracting
Suvrcru, HUMANSKU
Bronchus
Bronchus Bone marrow
Nasal sinus,
bronchus Bronchus Liver Bone m m w Bronchus
679
R~F~UE~NCE Mancuso?''
wagoncr et d 2 1 9
n u n et d..m minder et d.='
Hogstedt et al.=
Nelson et aLZu
GoldsmithP4
Brown," Bcrtazzi et d.=
MacMahon et al..m Epstcin and O z m o P
Finkelstein et al.." zambon CI al.,= Hcpkston.'6 &ldsmith et d.=
an alert but reassuring attitude toward exposed pa-
-tients. Agent-specific clinical interventions other
than the advice to limit further exposure to the extent
feasible (by using personal protective equipment of-
fered by the employer, for example) - are generally
unwarranted, although such patients may be enrolled
in company surveillance programs as part of ongoing
investigations or employee-monitoring policies.
The studies reviewed above focused on the effects of
specific chemicals or agents on the basis of previous
experiments in animals or observations in humans.
Efforts have also been made to evaluate the patterns of
disease in industries, trades, and occupational groups
with complex and mixed exposures to chemical and
physical agents. These investigations have demon-
strated the elevated risk of certain cancers in identified
populations without revealing the causal factor or fac-
tors. Important examples identified by several studies
include colorectal cancer in those who make the wood,
plastic, or metal models and patterns from which ma-
chines are
leukemia and lymphoma in
farmers,23'and glioblastoma multiforme in electrical
Innumerable cancer clusters or epide-
miologic associations between cancers and occupa-
tional groups have been reported; many remain un-
confirmed. Although specific prescriptions for disease
control or the evaluation of individual workers are
severely handicapped by the absence of an explana-
tion for these associations, concern among workers
and employers often runs high and must be addressed
by physicians. Efforts to reduce exposure to all work-
Place toxins (by good ventilation. for example), to-
Bether with education and screening. if the cancer site
amenable. have in our experience lessened anxiety;
h e effect on the risk or outcome of cancer remains
-Obscure. Finally. substantial progress has been made in late cancer control among workers shown to be at high risk virtue of past exposure. Late cancer control has
become increasingly important as more workers are notified of the health implications of confirmed cancer studies. The existence of large cohorts of chemical and textile workers exposed to benzidine with a known exceedingly high lifetime risk for bladder cancer has prompted the development of automated urine-cytology techniques to provide ongoing surveillance, with promising early results.234Similarly, the risk of colorectal cancer in model makers and patternmakers has prompted a novel study of the efficacy of serial sigmoidoscopic screening in the automobile industry, which employs many of these workers.235High-risk workers also figure prominently in new chemoprevention trials; the large number of men who were heavily exposed to asbestos provides an ideal population to study prospectively the effect of dietary and supplemental retinoids on lung cancer.236
P MNEW ROBLEMS IN OCCUPATIONAL EDICINE
Technological changes, current social perspectives, and historical events have put several new hazards and diseases into the spotlight in occupational medicine. Since these issues are likely to influence all but the most specialized clinical practices, we conclude this review with a brief summary of the field's current causes cdkbres.
Dioxin
No toxin more clearly epitomizes the public's dread of the chemical environment than 2,3,7,8-tetrachlorodibenzo-f-dioxin, usually referred to simply as dioxin. Its emergence as a potential occupational risk factor in Vietnam veterans who sprayed Agent Orange and other defoliants coincided with the rising awareness that environmental contaminants could insidiously
cause illness. On the basis of experiments in animals
thar show mutagenicity, neurotoxicity, and marked metabolic disruption at very low doses, virtually every conceivable adverse health outcome has been suspect-
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THE N E W ENGLANDJOURNAL OF MEDICINE
March 3. 19%
ed among exposed veterans, chemical workers making herbicides and wood preservatives, and the victims of environmental accidents in which materials containing dioxin have leaked or spilled, such as that at Seveso, Italy, in 1976.
More than a decade of intensive research, including the epidemiologic study of those identifiable as the
most heavily exposed - workers with the disfiguring acneiform lesions known as chloracne - has left a
surprisingly different picture. Although the final word is surely not in, some conclusions seem secure. Other than a possible excess of soft-tissue sarcoma or lym-
neither cancer nor any other cause of death seems to be occurring in e x c e s ~ . ~M~or~bi~d * effects, including mild chronic liver and peripheralnerve dysfunction, as well as altered lipid and porphyrin profiles, appear to be slight and limited largely to those who were most intensely exposed (especially those with c h l o r a ~ n e ) . *T~h~e*se~ ~findings are far from definitive, but confirmation by additional observations would suggest that humans are less susceptible to this dreaded toxin than the results of studies in animals would have predicted. An analytic technique to measure the amount of dioxin in tissue (in parts per trillion) has been developed and validated`45 and should greatly facilitate the further study of this contaminant in humans.
VidecbDisplay Terminals
Since their widespread introduction into offices in the past decade, video-display terminals have had a profound effect on every aspect of work. In the resulting upheaval, many questions have been raised about their safety, with effects ranging from the predictable
- eye strain, musculoskeletal symptoms, and emotional stress - to the unpredictable: skin disorders
(maculopapular facial rashes) and adverse reproduction outcomes (birth defects and spontaneous abortions, for example). Dozens of reports, studies, and conferences have addressed these issues around the world.
The current consensus suggests that work with video-display terminals is associated with an increase in subjective ocular problems, including pain, burning, and irritation, and transient visual disturbances, including blurring, diplopia, and altered light accommodation. O n the other hand, no chronic disorders (myopia or cataracts, for example) have been confirmed.246s24S7imilarly, the operators of video-display terminals are as prone to musculoskeletal symptoms as other clerical workers, probably because of poorly designed workstations and f ~ r n i t u r e . M~ o~o.d~d~is~turbances are probably due to problems in job design rather than to exposure to the video-display terminal i t ~ e l f . * ~T~h,e~c~a'use of the rashes occasionally observed in operators is uncertain; therapy may nonetheless include trials of job modification or removal from exposure, since no alternative explanation has emerged.252Finally, despite some widely publicized
clusters. insufficient data exist to incriminate video-
display terminals as teratogen^.'^^.^^^ The possibility
of an increased risk of spontaneous abortion has been raised,'53 but reducing exposure in pregnant women is probably not vet warranted on the basis of the information available.
Sick-Building Syndrome
An unforeseen consequence of the fuel conservation measures that followed the oil shortage of the 1970s was the concentration of common pollutants
in "tight" buildings served by closed systems of ventilation. In the late 1970s and 1980s, outbreaks of illness characterized by intractable upper respiratory symptoms, ill-defined central nervous system dysfunction, and low morale and productivity have occurred in countless offices. Although the evaluation of individual patients is typically unrevealing, the epidemiologic pattern of illness unmistakably incriminates the workplace.255Unfortunately, early attempts to investigate the outbreaks generally failed, raising the diagnostic possibility of mass psychogenic illness.
With the increased frequency of reports, however, the evidence became overwhelming that environmental factors, including smoke, formaldehyde, oxides of nitrogen, microorganisms, and climate, were culpable, sometimes singly but more often in concert.256 Results of the investigations of hundreds of outbreaks demonstrate a correlation between symptoms and airborne levels of carbon dioxide, which is not the cause of illness but a marker of inadequate ventilation. The best evidence indicates that the solution is usually straightforward, involving the elimination or reduction of indoor sources of pollutants, the regular cleaning and filtering of ventilation systems, and an increase in the proportion of fresh rather than recirculated air.257 Although palliative job changes or medication may be indicated in some patients, especially those who are highly atopic or sensitive, the focus of treatment should be on the building, not the victim.
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Multiple Chemical Sensitivities
The most puzzling clinical entity emerging in the 1980s is the syndrome of ostensible allergy or sensitivity to almost all organic and synthetic chemicals.258
Patients, typically previously healthy people, U S U ~ Y
present during a sick-building outbreak or in the aftermath of an accidental overexposure to an established toxin (a solvent, irritant gas, or pesticide, for example) and report recurrent, intensified symptoms to progressively smaller amounts of the toxin, often mere traces of the original offender. Workups fail to reveal physip logic abnormalities to explain these sequelae, but generalization begins to occur, with a broader array of symptoms, almost invariably including symptoms Of the central nervous system, in response to an expanding repertoire of chemical stimuli. Many patients
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OCCUPATIONAL MEDICINE - CULLEN E T AL.
68 1
are unable to work because of their responses to
even well-controlled workplace substances. In extreme cases, patients become environmental exiles from modem life.
Although the data are sparse, a sufficient number of
such cases have occurred to spur the development of a subculture of practitioners called clinical ecologists or
environmental physicians. Armed with unproved theories and diagnostic tests that demonstrate that the immunosuppressive effects of an excessive "total-body burden" of organic chemicals cause "environmental illness" or "20th-century disea~e,"~~~*~t@he-s'e practitioners encourage patients to avoid contamination and may offer various treatments, including nutritional supplementation, anticandidal medication, and regimens for increasing the turnover of fat-borne chemicals with long biologic half-lives.
Although data have been presented to refute the claimed immunogenic basis of the illness261and to provide a1ternative diagnoses in some cases,262the disorder does appear to be prevalent and often devastating, particularly with respect to occupational functioning, since the work environment cannot readily be controlled by the patient. Unfortunately, although there is real controversy, most practitioners remain unaware of the problem or skeptical, and little con-
structive investigation has been reported. Descriptive studies have attempted to characterize small subgroups of patients in psychological terms, considering the disorder as a variant of post-traumatic stress d i ~ o r d e ?o~r~ "psychological sensitization to the workplace."264Coliaborative efforts to define the
problem -like those recently undertaken for the pos-
jibly related chronic fatigue syndrome265- could
ierve to legitimize and stimulate future research. Meanwhile, the placebo value of radical therapies rlotwithstanding, most therapeutic effort has been supportive, encouraging patients to improve their functioning through tolerance and understanding of [he symptoms.
REFERENCES
33. Schaumburg HH, Spencer PS. Thomas PK. Disorders of peripheral nerves. Philadelphia: F.A. Davis, 1983.
34. Boor JW. Hunig H. Persistent cerebellar ataxia after exposure to toluene. Ann Neurol 1977; 2440-2.
!35. Braceland FJ. Mental symptoms following carbon disulphide absorption and intoxication. Ann Intern Med 1942; 16:246-61.
136. Perlstein MA, Attala R. Neurologicsequelae of plumbism in children. Clin Pediatr 1966; 5292-8.
3J Axelson 0. Hane M, Hogstedt C. A case-referent study on neuropsychiatnc disorders among workers exposed to solvents. Scand J Work Environ Health 1976:?:14-20.
31( Olsen J. S a b r a S.A case-reference study of neuropsychiatric disorders among workers exposed to solvents in the Danish wocd and furniture Industry. Scand J Soc Med Suppl 1980: 1644-9.
iy. Rodin `J. Edling C. Axelson 0. Clinical studies of psychoorganic syndmmes among workers with exposure to solvents. Am J Ind Med 1984; 5287-95.
w. Orback P. Lindgrcn M. Olivecrona H. Haeger-Aronsen B. Computed to-
mography and psychomemc Lest performances in patients with solvent Induced chronic encephalopathy and healthy controlb. Br J Ind Med 1987: 44: 175-9. " SePpaliunen AM. Neurophysiological aspects of the toxictry of organic ~ l v e n t s .Scand J Work Environ Health 1985: I I:Suppl l : 6 l 4 .
142. Jensen PB. Nielsen P, Nielsen NO, Olivarius BD. Hansen JH. chronic toxic encephalopathy following occupational exposure to organic solvents:
the course after cessation of exposum illustrated by a neurophysiological
follow-up study. Ugeskr Lacger 1984; 146:1387-90. 143. Arlien-Seborg P. Bruhn P. Christensen EL. Glydensted C. Damganrd M.
Chronic painters' disease: a follow-up study of 26 former h o u r paintm with occupational toxic encephalopathy. Ugeskr Lacger 1981; 1433306974.
144. Mahoney FC. Moore PA. Baker EL, Lea R. Experimental n i m oxidc exposure as a model system for evaluating newbehavioral tests. Toxicol-
ogy 1988: 49449-51.
145. Cherry N, Hutchins H, Pace T, Waldron HA. NeurokhaviourPl effectrot
repeated occupational exposure to toluene and paint solvents. Br J Lnd Med 1985; 42:291-300. 146. Waldron HA. Solvents and the brain. Br J Ind Med 1986.43734. 147. Shalat SL.Seltzer B. Pidcock C, Baker EL Jr. Risk factors for Alzheimer's diseasc: a case-control SNdy. Neurology 1987; 37:1630-3. 148. Spencer PS, Schaurnburg HH. Organic solvent neunxoxicity: fons .ad research needs. Scand J Work Environ Health 1985; 1I:Suppl 153-60. 149. Longsmth WT Jr, Rownstock L, Heyer NJ. P o m m palsy? Neurologic disorder in thnt aluminum smelter workers. Arch Intern Med 1985; 145:1972-5.
150. Manyn CN, Barker DJP, Osmond C, Harris EC. E d w h n JA. h e y RF.Geographical relation between Alzheimer's disease and aluminium in
drinking water. Lancet 1989; 159-62. 151. Rozman K. Hanninen 0, eds. Gastrointestinal toxicology. Amaerdun:
Elsevier, 1986.
152. Rcdlich CA. Becken WS, Sparer J. et al. Liver disease associated with occupational exposure to the solvent dimethylfonnamide. Ann lntcm Med
1988; 108:680-6.
-7
153. Bastian PG.Occupational hepatitis caused by methylenedianilinc. Med J
-Aust 1984; 141:533-5.
154. Dsuing M, Ranek L. Isolated liver damage in chemical workers. Br J Ind
Med 1984; 41:1424.
155. Thiele DL. Another cause of toxic liver injury. Gasaoenterology 1989; %:537-8.
156. Schenker MB, SamuelsSJ. Perkins C. Lewis EL, Katz DF. OventreaJW.
`
Respective surveillance of semen quality in the workplace. J Occup Med 1988; 30:336-44. 157. Wilcox AJ, Weinberg CR, O'Connor JF. et al. Incidence of early loss of pregnancy. N Engl J Med 1988; 319:189-94. 158. Whonon D, Milby TH, Krauss RM, Stubbs HA. Testicular function in
DBCP exposed pesticide workers. J &cup Med 1979; 21:161-6.
159. Cullen MR. Kayne RD, Robins JM. Endocrine and reproductive dysfunction in men associated with occupational inorganic lead intoxication. Arch Environ Health 1984; 39:43140.
160. Assennato G , Paci C, Baser ME. et al. Sperm count suppression without
endocrine dysfunction in lead-exposed men. Arch Environ Health 1986; 41:387-90. 161. Lancranj.~1~. Alteration of spermatic liquid in patients chronically poisoned by carbon disulphide. Med Lav 1972: 6329-33. 162. Landrigan PJ, Meinhardt TJ,Gordon J. et al. Ethylene oxide: an overview of toxicologic and epidemiologic research. Am J Ind Med 1984; 6:103-15. 163. Eljack AH, Hrudka F. Patterns and dynamics of teratospermia induced in
rams by parenteral treatment with ethylene dibromide. J Ultrastruct Res 1979: 67:124-34. 164. Lee 1P. Effects of environmental metals on male reproduction. In: Clark-
son TW,Nordkrg GF, Sager RR. eds. Reproductive and developmental
toxicity of metals. New York: Plenum Press. 1983:253-78. 165. RodamilansM. Osaba MJ. To-Figueras J. et al. Lead toxicity on endocrine
testicular function in an occupationally exposed population. Hum Toxicol 1988; 7:125-8.
166. Finkelstein JS, McCully WF, MacLaughlin DT, Godine JE, Crowley WF
Jr. The mortician's mystery: gynecomastia and reversible hypogonadotropic hypogonadism in an embalmer. N Engl J Med 1988; 318:%15.
167 Cohen EN. Gift HC. Brown BW. et al. Occupational di- in dentistry and chronic exposure to trace anesthetic gases. J Am Dent Assoc 1980; 101:21-31.
168. Axelsson G. Jeansson S, Rylander R. Unander M. Regnancy abnormalities among personnel at a virological laboratory. Am J Ind Med 1980. I :129-37
169. Clarkson TW. Nordterg GF. Sager PR. Reproductive and developmental
toxicity of metals. Scand J Work Environ Health 1985: 11:145-54. 170. Axelson 0. Edling G.Andersson L. Pregnancy outcome among women in
a Swedish rubber plant. Scand J Work Environ Health 1983: 9Suppl2:79-
83
171. Pastides H. Calabrese U.Hosmer DW Jr. Harris DR Jr. Spontaneous
abortion and general illness symptoms among semiconductor manufacturers. J Occup Med 1988: 30543-51.
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i
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THE NEW ENGLAND JOURNAL OF MEDICINE
March I(. 1'1w1
172. Goulet L. Theriault G. Association between spontanmus abortion and ergonomic factors: a literature review of the epidemiologtc evidence. Scand J Work Environ Health 1987: 13:399403.
173. Manton WI. Total conmbution of airborne lead to blood Id.Br J Ind Med
1985:42:168-72. 174. Eskenazi B. Bracken MB. Holford TR. Grady J. Exposure to organic
solvents and hypertensive disorders of pregnancy. Am J Ind Mcd 1988; 14:177-88.
175. Hadler NM. Industrial rheumatology: clinical investigations into the influence of the pattern of usage on the panern of regional musculoskeletal disease. Arthritis Rheum 1977: 2 0 1019-25.
176. K a a JN, Liang MH. Carpal tunnel syndrome and the workplace: epidemiologic and management issues. Intern Med 1988:9 6 7 3 .
177. Falck B. Aamio P. Left-sided carpal tunnel syndrome in butchers. Scand J Work Environ Health 1983;9291-7.
178. Armsmng TJ. Chaffin DB. Carpal tunnel syndrome and selected personal attributes. J Occup Med 1979: 21:481-6.
179. Masear VR. Hayes JM. Hyde AG. An industrial cause of carpal tunnel syndrome. J Hand Surg [Am] 1986; I1:222-7.
180. Kaplan PE. Carpal tunnel syndrome in typists. JAMA 1983;250821-20. 181. Cannon U,Bernacki EJ. Walker SD. Personal and occupational factors
associated with the carpal tunnel syndrome. J Occup Med 1981;2 3 3 5 - 8 . 182. Silverstein BA. Fine U, Armstrung TJ. Occupational factors and carpal
tunnel syndrome. Am J Ind Med 1987;I1:343-58. 183. Armsmng TJ. Chaffin DB. Foulke JA. A method for documenting hand
positions and forces during manual work. J Biomech 1979 12:131-3. 184. Feldman RG. Goldman R. Keyserling WM. Peripheral nerve entrapment
syndromes and ergonomic factors. Am J Ind Med 1983;4661-81. 185. Gelberman RH, Szabo RM, Williamson RV, Dimick MP. Sensibility test-
ing in peripheral-nerve compression syndromes: an experimental study in humans. J Bone Joint Surg [Am] 1983;65632-8. 186. Szabo RM. Gelberman RH. Williamson RV. Dellon AL, Yam NC, Dimick MP. Vibratory sensory testing in acute peripheral nerve compression. J Hand Surg [Am] 1984:9A:104-9. 187. Lundborg G. Myers R, Powell H. Nerve compression injury and increased endoneuria1 fluid pressure: a "miniature compartment syndrome." 1Neuml Neurosurg Psychiatry 1983: 46:I I 19-24. 188. Grundberg AB. Carpal tunnel decompression in spite of normal electromyography. J Hand Surg [Am] 1983;8:34&9. 189. Spindler HA, Dcllon AL. Nerve conduction studies and sensibility testing in carpal Nnnd syndrome. J Hand Surg [Am] 1982,7260-3. 190. Golding DN, Rose DM. Selvarajah K. Clinical tests for carpal Nnml syndrome: an evaluation. Br J Rheumatol 1986 26388-90. 191. l'yykko 1. Clinical aspects of the hand-arm vibration syndrome: a review. Scand J Work Envimn Health 1986 1243947. 192. Olson N. Diagnostic tests in Raynaud's phenomena in workers exposcd to vibration: a comparative study. Br J Ind Med 1988:45426-30.
,193. Ekenvall L. Lindblad LE. Is vibration white finger a primary sympathetic nerve injury? Br J Ind Med 1986: 43:702-6.
194. Brammer AJ. Pyykko 1. Vibration-induced neuropathy: detection by nerve conduction measurements. Scand J Work Environ Health 1987; 13:317-22.
195. Rydevik B, Lundborg G. Baggc U. Effects of gradcd compression on intramural blood flow: an in vivo study on rabbit fibial nerve. J Hand Surg [Am] 1981;6:3-12.
I%. Ekenvall L. Carlsson A. Vibration white finger: a follow-up study. Br J Ind Med 1987;44:476-8.
197. Melick WF, NarykaJ1. Kelley RE. BladdercancerduetoexpoJurctoparaaminobiphenyl: a 17-year follow-up. J Urol 1971; 106:220-6.
198. Pinto SS. Henderson V. Enterline PE. Mortality experience of arsenicexposed workers. Arch Environ Health 1978;33:325-31.
199. Figueroa WG. Raszkowski R. Weiss W. Lung cancer in chloromethyl methyl ether workers. N Engl J Med 1973: 288:1096-7.
ZOO. Case RAM, Hosker ME. McDonald DB, Pearson JT. Tumours of the urinary bladder in workmen engaged in the manufacture and use of certain dyestuff intermediates in the British chemical industry. Pan 1. The role of aniline. benzidine. alpha-naphthylamine. and beta-naphthylamine. Br J Ind Med 1954: 11:75-104.
201. Hayes RB. Review of occupational epidemiology of chromium chemicals
and respiratory cancer. Sci Total Environ 1988: 71:331-9. 202. National Research Council. Health effects of exposure to ionizing radi-
ation. (BEIR V). Washington, D.C.: National Academy Press. 1989. 203. Idem. Health risks of radon and other internally deposited alpha erniners:
BEIR IV. Washington. D.C.: National Academy Press. 1988. 204. Polednak AP. Stehney AF. Rowland RE. Mortality among women first
employed before 1930 in the US radium dial-painting industry: a group ascertained from employment lists. Am J Epidemiol 1978: 107179-95, 205. Grandjean P. Andersen 0. Nielsen GD.Carcinogenicity of occupational nickel exposures: an evaluation of the epidemiologic evidence. Am J Ind Med 1988: 13:193-209. 206. Hammond EC. Selikoff IJ. Lwther PL. Seidman H. Inhalation of benzpyrene and cancer in man. Ann N Y Acad Sci 1976 271:116-24.
207. Waxweiler RJ. Stnnger W. Wagoner JK. Jones J. Falk H. Cmer c
Neoplastic risk among workers exposed to vinyl chloride. Ann N Y
Sci 1976 271:u)-8. 208. Acheson ED. Pippard EC. Winter PD. Mortality of English furnirurr mak.
en. Scand J Work Environ Hcalth 1984, IO21 1-7.
709. Roc FJ. Occupational cancer: where now and w h m next? Scand J work
Environ Health 1985: 11:181-7. 710. Doll R. Pet0 R. The causes of cancer: quantitative estimates or avo,dilnlr
risks of cancer in the United States today. 1 Natl Cancer lnst 19x1
66:1191-308.
211. Checkoway H. Pearce N. Crawford-Brown DJ. Cragle DL. Radiation doscs and caw-specific mortality among workers at a nuclear material,
fabrication plant. Am J Epidemiol 1988: 127:255-66. 212. Checkoway H. Mathew RM. Shy CM. et al. Radiation. work experience,
and cause specific mortality among workers at an energy research labonto.
ry. Br J Ind Med 1985;42525-33. 213. Kneale GW, Mancuso TF,Stewan AM. Job related mortality risks
Hanford workers and their relation to cancer effects of measured doses
external radiation. Br J Ind Med 1984 41:9-14. 214. Sotahan T. Burges DC,Waterhow JA. A mortality study of nickellchre
rnium platers. Br J Ind Med 1987; 44230-8. 215. MacKerer CR. Health effects of oil mists: a brief review. Toxicol ind
Health 1989:5:429-40. 216. Stecnland K. Lung cancer and diesel exhaust: a review. Am J Ind Med
1986 IO 171-89.
217. Boffena P. StellmanSD. Garfinkel L. Diesel exhaust exposure and mortal.
ity among males in the American Cancer Society prospective study. Am J Ind Med 1988; 14403-15.
218. Mancuso TF.Mmality study of beryllium industry workers' occupational lung cancer. Envimn Res 1980 21:48-55.
219. Wagoner JK. Infante PF, Bayliss DL. Beryllium: an etiologic agent in h e induction of lung cancer. nonneoplastic respiratory disease. and h e m dis-
ease among industrially exposcd workers. Envimn Res 1980 21:15-34. 220. Thun MI. Schnorr TM. Smith AB. Halperin WE. Lemen RA. Monalic
-among a cohon of U.S. cadmium production workers an update. J Nail
Cancer lnst 1985:74325-33. 221. Elinder CG,Kjellsmm T. Hogstedt C. Andersson K, Spang G. Cancer
mortality of cadmium workers. Br J Ind Med 1985;42651-5. 222. Hogsvdt C,Aringer L. Gustavsson A. Epidemiologic support for ethylen:
oxide as a cancer-causing agent. JAMA 1986 255:1575-8. 223. Nelson N, Levine R1. A l k n RE, et al. Contribution of formaldehyde to
respiratory cancer. Environ Health Pmpcct 1986; 7023-35. 224. Goldsmith JR. Comparative epidemiology of men exposed to asbestos and
man-made mineral fibers. Am J Ind Mcd 1986 10543-52. 225. Brown DP. M o d i t y of workers e x p o d to polychlorinated biphenyls -
an update. Arch Environ Health 1987;42333-9.
226. Bertazzi PA. Riboldi L. Pesatori A, Radice L, k h e t t i C. Cancer m d ity of capacitor manufacturing workers. Am J Ind Med 1987;11:165-76.
227. MacMahon B. Monson RR. Wang HH. Zheng Tt. A second follow-upof
mortality in a cohort of psticide applicators. J Occup Med 1988 3042932. 228. Epstein SS. Ozonoff D. Leukemias and blood dyscrasias following u;P
SUR to chlordane and heptachlor. Tentogenesis Carcinog Mutagen 1987; 75274.
229. Acquavella JF. Douglass TS,Phillips SC. Evaluation of excess c o l o d cancer incidence among workers involved in the manufacture of polypfQpylene. 1 Occup Med 1988;3043842.
230. Swanson GM. Belle SH. Burrows RW Jr. Colon cancer incidence amOng
modelmakers and patternmakers in the automobile industry: a cOndnU& dilemma. J Occup Med 1985;27567-9. 231. Blair A. Malker H, Cantor KP. Burmeister L, Wiklund K. Cancer among farmers: a review. Scand J Work Environ Health 1985; I I:39747. 232. Thomas TL. Stolley PD. Stemhagen A, et al. Brain tumor mortality ri*
among men with electrical and elecmnicsjobs: a casc-conrml study. J Nd Cancer lnst 1987;79233-8. 233. Lin RS. Dischinger PC.Conde J. Famll KP. Occupational exposun to elechomagnetic fields and the occurrence of brain tumm: an analysis Of possible associations. J Occup Med 1985;27:413-9.
234. Hemsacet GP 111. West SS. Wecm WL. et al. Quantitatiw f l u o W e M measurements of AO-stained normal and malignant bladder cells. ItM Cancer 1983;3 1577-85.
235. Hoar SK. Bang KM. Tillen S,Rodriguez M. Cantor KP, Blair A. screen-
ing for colorectal cancer and polyps among panern workers. J @CUP MCd 1986;28:704-8.
236. Omenn GS.Goodman GE. Kleinrnan GD, et al. The role of inUWndon studies in ascertaining the contribution of dietary factors in lung Canccc rhc
Seattle chemoprevention trial of retinoids in asbestos-exposed Workcn' Ann N Y Acad Sci 1988;534575-83.
237. Hardell L. Sandstrom A. Case control study: soft tissue Sarcomas and
exposure to phenoxyacetic acids or chlorophenols. Br J Cancer Ifl' 3971 1-7.
7
vel. 322 NO. IO
CASE RECORDS OF THE MASSACHUSETTS GENERAL HOSPITAL
683
238. Fingerhut MA, Halpcrin WE. Honchar PA. Smith AB. Groth DH, Russell WO. An evaluation of reports of dioxin exposure and soft tissue -ma pathology among chemical W O ~ ~ CiKn the United States. Scand J Work Environ Health 1984; 10:299-303.
239. Hoar SK, Blair A, Holmes R.et al. A g r i c ~ l t u ~he4rbicide use and risk of
lymphoma and soft-tissue sarcoma. JAMA 1986; 2561 141-7. 240. Zack JA, Suskind RR. The mortality experience of workers exposcd to
ternrchlorodibenzodioxinin a trichlorophenol prcccss accident. J Occup
Med 1980; 22:I 1-4. 241. Thiess AM, Frentzel-Beyme R. Link R. Mortality study of persons ex-
posed to dioxin in a mchlorophenol-proccss accident that occurred in the BASF AG on November 17. 1953. Am J Ind Med 1982; 3:179-89. 242. Oa MG, Holder BB, Olson RD. A mortality analysis of employees engaged in the manufacture of 2.4.5-mchlorphcnoxy-Pc acid. J Occup Med 1980; 2 4 7 - 5 0 .
243. Suskind RR. Chloracne, 'The hallmark of dioxin intoxication." Scand J Work Envimn Health 1985; 11:165-71.
244. Larhmp GD. Machado SG. Karrison, et al. Air Force Hcalth Study: an cpidcmioIogicinvestigationof health effects in AiForcep m o ~ eflollowing expowr to herbicides: first followup examination resultr: summary qat. Brooks Air Force Base, Tex.: Epidemiology Division, USAF School of Aemspace Medicine, Human Systems Division, 1987. (National Technical lnfonnation Services document no. AD A 189 799 OXSP.)
245. Patterson DG Jr. Hampton L. Lapaa CR Jr, et al. High-resolution gas chromatogmphidhigh-resolutionmass specmmVic analysis of human sem on a whole-weight and lipid basis for 2.3,7,8-tcwchlomdiknso-p
dioxin. Anal Chem 1987; 59:2000-5. 246. Rey P, Meyer JJ. Visual impairments and their objective comlpces. In.
Grandjean E, Vigliani E, eds. Ergonomic aspects of visual display m i -
nals. London: Taylor & Francis, 1982:77-83. 247. Panel on Impact of Video Viewing on Vision of Workers,Committee on
Vision, Commission on Behavioral and Social Sciences and Education, National Research Council. Video displays, work, and vision. Washington, D.C.: National Academy Press. 1983. 248. Hunting W. Laubli T. Grandjean E. Postural and visual loads at VDT workplaces. I. Constrained posturn. Ergonomics 1981; 24917-31. 249. Starr SJ. A study of video display terminal workers. 1Occup Med 1983; m.95-8.
250. Johansson G.Aronsson G. Smss reactions in computerizedadministrative work. J Occup Behav 1984; 5:159-81.
251. B q q v i s t UO. Video display terminals and health: a technical and medical appraisal of the state of the arc. Scand J Work Environ Heallh 1984, IOSUppl 255-7.
252. Idem. Video display terminals and health: a technical and medical appraisal
of the state of the an.Scand J Wwk Environ Health 1984; IOSuppl257-
9. 253. Goldhabcr MK, Polen MR. Hain RA. The risk of miscarriage and birth
defects among women who use video display terminals during pregnancy.
Am 1 Ind Med 1988; 13:695-706.
254. Kurppa K. Holmberg PC,Rantala K,Nurmincn T, Saxen L. Birth defects and exposure to video display terminals during pregnancy: a Finnish case-
referent study. Scand J Work Environ Health 1985; I1:353-6. 255. Whonon MD, &on SR. Gordon NJ. Morgan RW. Investigation and
work-up of tight building syndrome. J &cup Med 1987: 29142-7. 256. Burge S. Hedge A, Wilson S. Bass JH, Robertson A. Sick building
syndrome: a study of 4373 office workers. Ann Occup Hyg 1987; 31:493-
504.
257. Sparer J. Environmental evaluation of workers with multiple chemical sensitivities: an indusaial hygienist's view. State Art Rev Occup Mcd 1987: 2:705-12.
258. Cullen MR. The worker with multiple chemical sensitivities:an overview. State AR Rev Occup Med 1987; 2655-61.
259. Trowbridge JP, Walker M. The yeast syndrome. New York: Bantam Books, 1986.
260. Bell IR. Clinical ecology: a new medical approach to environmental illness. Bolinas, Calif.: Common Knowledge Press, 1982.
261. Ten AI. Environmentalillness: a clinical review of fifty cases. Arch Intern Med 1986 146:145-9.
262. Bmdsky C. "Allergic to everything": a medical subculture. Psychosomatics 1983; 24:731-42.
263. Schottenfeld RS. Cullen MR. Recognition of occupation-induced post aaumatic stress disorders. J Occup Med 1986 28:365-9.
264. Shusterman D. Belmes J. Cone J. Behavior sensitization IO irrimts/odorants after acute overexposures. J Occup Med 1988; 30565-7.
265. Homes GP. Kaplan JE. Gantz NM, et al. Chronic fatigue syndrome: a working case definition. Ann Intern Med 1988; 108:387-9.
CASE RECORDS
OF THE MASSACHUSETTS GENERAL HOSPITAL
Weekly Clinicopathological Exercises
FOUNDED BY RICHARD C . CABOT
ROBERT E. SCULLY. M.D., Editor EUGENE J . MARKM, .D.. Associate Editor WILLIAMF. MCNEELYM, .D.. Associate Editor
BETTY U. MCNEELYds,sistant Editor
CASE 10-1990 PRESENTATION OF CASE fz 15-year-old girl was admitted to the hospital be-&useof pain in the riqht wrist and multiple radiolucnt bony defects. The patient was in apparent good health except for
scoliosis. for which she was seen in periodic orthopedic follow-up examinations. Three days before admission, on a routine visit to her orthopedist, she mentioned pain in the right wrist of approximately one year's duration. with worsening on vigorous use of the right upper extremity. Physical examination revealed no swelling or tenderness of the wrist. X-ray films of the right wrist (Fig. 1) showed a well-circumscribed osteolytic lesion, 5 mm, with thickening of the overlying cortex, 7 cm proximal to the distal end of the ulna; a poorly circumscribed osteolytic area, 1.5 cm, was seen in the distal radial metaphysis; no cortical reaction or expansion was detected. Several days later x-ray films of the left wrist revealed a lesion with similar features, 2.5 cm, in a comparable location in the distal left radius. The girl was referred to this hospital.
The patient gave a history of incision and drainage of a left axillary lymph node at the age of two years and of a febrile seizure at about the same age; phenytoin sodium was administered for 11/2 years, without recurrence of a seizure. She reported a very mild, intermittent cough in spring and fall that usually responded to antihistamine medications. Ten months before entry she consulted her physician because of acute pain in a rib. without known trauma. An s-ray film of the chest was reported to show a healing rib fracture. There was a histor) of malignant tumors in many pacernal relatives. including thr patient's
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